Direct and Residual Effect of Organic Manure on Buckwheat (Fagopyrum Esculentum Moench) – Fodder Ricebean (Vigna Umbellata) Cropping System

D. Mahata1, P.S. Patra2*, A. C. Sinha3, A.K. Singha Roy3, S. Bandyopadhyay3

1Gramin Krishi Mousam Sewa, AMFU-Pundibari, Uttar Banga Krishi Viswavidyalaya, Cooch Behar.

2Assistant Professor (Agronomy), Regional Research Station, Terai Zone, Uttar Banga Krishi Viswavidyalaya, Pundibari, Cooch Behar, West Bengal, India.

3Department of Agronomy, Uttar Banga Krishi Viswavidyalaya, Pundibari, Cooch Behar, West Bengal, India.

Corresponding author Email: parthaagro@gmail.com

DOI : http://dx.doi.org/10.12944/CARJ.6.1.08

Article Publishing History

Received: 02/08/2017
Accepted: 11/02/2018
Published Online: 14-02-2018

Review Details

Plagiarism Check: Yes
Reviewed by: Dr. Bharat Meena
Final Approval by: Dr. Avtar Singh Bimbraw

Article Metrics

Views     PDF Download PDF Downloads: 1233

Google Scholar

Abstract:

The research programme was carried out during early summer seasons of 2012 and 2013 at the experimental farm of Uttar Banga Krishi Viswavidyalaya, Pundibari, Cooch Behar to study the direct and left over effect of organics on Buckwheat (Fagopyrum esculentum Moench) – fodder Rice bean (Vigna umbellata) cropping system. The trial was carried out in Randomized block design with 14 treatments and replicated thrice. Results demonstrate that combined application of vermicompost, poultry manures, mustard cake and farmyard manure improved seed yield of buck wheat by 0.51 and 0.53 t ha-1 over 100 % RDF in 2012 and 2013, respectively. Among the sole application of organic manures, application of poultry manure at 5 t ha-1 proved its superiority in terms of stem and seed yield of buck wheat. Collective application of vermicompost at 2.5 t ha-1 + mustard Cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 +  Farmyard manure at 4 t ha-1  to the preceding buckwheat crop produced 18.67 and 17.20% more fodder yield of ricebean than 100 % chemically treated plot during both the years. Application of vermicompost at 2.5 t ha-1 + mustard Cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 +  Farmyard manure at 4 t ha-1  also leave  highest amount of  available N, P and K in the soil. Economic analysis revelaed that treatment producing highest yield of buck wheat and ricebean fetched lower B: C ratio (0.63 and 0.74 during 2012 and 2013, respectively) as compared to other treatemnts.

Keywords:

Buckwheat; Mustard Cake; Organic Manure; Poultry Manure and Ricebean

Download this article as: 

Copy the following to cite this article:

Mahata D, Patra P. S, Sinha A. C, Roy A. K. S, Bandyopadhyay S. Direct and Residual Effect of Organic Manure on Buckwheat (Fagopyrum Esculentum Moench) – Fodder Ricebean (Vigna Umbellata) Cropping System. Curr Agri Res 2018;6(1). doi : http://dx.doi.org/10.12944/CARJ.6.1.08

Copy the following to cite this URL:

Mahata D, Patra P. S, Sinha A. C, Roy A. K. S, Bandyopadhyay S. Direct and Residual Effect of Organic Manure on Buckwheat (Fagopyrum Esculentum Moench) – Fodder Ricebean (Vigna Umbellata) Cropping System. Curr Agri Res 2018;6(1). Available from: http://www.agriculturejournal.org/?p=3486


Introduction

Organic manures have traditionally been the important input as sources of plant nourishment. Organic manures directly provided macro and micronutrient and indirectly facilitates in improving the physical, chemical and biological properties of soils.1 These manures, containing all the essential nutrients when applied to the preceding crop, leave the residual effect and this benefit is harvested by the succeeding crop to a great extent.2 Organic matter is the heart of fertile soil. It helps in increasing cations and anions holding capacity of soil particularly phosphorus and nitrates. Throughout the crop growth period these adsorbed nutrient ions are slowly available for the benefit of crop. Use of organic matter plays a significant role in improving the use efficiency of applied nutrients and thereby reducing the expenditure of nutrient. Organic manuring has also been reported to improve the efficiency of nitrogenous fertilizers in acidic soils.Buckwheat (Fagopyrum esculentum Moench) is a very old Asian crop, extensively grown throughout the globe. It is an important underutilized crop, plays a crucial role in meeting up the food security of the temperate and hilly regions of the countries in East Asia, East Europe and the Himalayan region.4 Though it is not a cereal, but the starchy seeds are generally classified among the cereal grains as of their similar usage. Ricebean (Vigna umbellata ) is a disease & insect resistant, fast growing legume crop and has the capability to produce huge amounts of healthy animal feed and high quality grain. Its cultivation is mainly confined to the Western, Northern and Eastern India and Nepal. It is broadly grown as an intercrop, predominantly of maize, and was traditionally being grown on residual moisture after rice. Ricebean can grow successfully in the large range of soils. Keeping the above facts in mind present experiment has been carried out to see the, direct and left over consequence of organics on the growth, yield and economics of buckwheat-ricebean cropping sequence.

 Materials and Methods

This research trial was undertaken at the Research Farm of Uttar Banga Krishi Viswavidyalaya, Pundibari, Cooch Behar, West Bengal, India. The farm is located at 26019’86” N latitude and 89023’53” E longitude and at an elevation of 43 meters above mean sea level. The soil of the research plot was sandy loam in texture and acidic in nature having pH of 5.5. The initial organic carbon 0.639%, available nitrogen 107.59 kg ha-1, available phosphorus 15.36 kg ha-1 and available potash 71.68 kg ha-1 were recorded before buck wheat cultivation in 2012. In the first year buck wheat variety VL-7 was sown during mid January with a row and plant distance of 30 cm X 7-10 cm. Fourteen treatments were allocated in randomized complete block design and replicated thrice. Treatments comprises of T1 = Control (No manures/no fertilizers), T2 = RDF (40:20:20), T3 = Vermicompost @ 2.5 t ha-1, T4 = Vermicompost at 5 t ha-1,  T5 = Mustard Cake @ 2.5 t ha-1, T6= Mustard Cake @5 t ha-1, T7 = Poultry Manure @ 2.5 t ha-1, T8 = Poultry Manure @ 5 t ha-1, T9 = F.Y.M @ 8 t ha-1,  T10 = RDF +FYM @ 4 t ha-1, T11 = Vermicompost @ 2.5 t ha-1 + Mustard Cake @ 2.5 t ha-1, T12 = Vermicompost @ 2.5 t ha-1 + Mustard Cake @ 5 t ha-1,  T13 = Vermicompost @ 2.5 t ha-1 + F.Y.M @ 4 t ha-1 and T14 = Vermicompost @ 2.5 t ha-1 + Mustard Cake @ 2.5 t ha-1 + Poultry Manure @ 2.5 t ha-1 +  F.Y.M @ 4 t ha-1. Nutrient concentration of vermicompost, mustard cake, poultry manure and FYM were N: P: K., 1.15:0.48:0.72, 3.76:0.71:0.76, 2.71:2.31:2.10 and 0.56:0.18:0.52 respectively.  After the harvest of buck wheat, ricebean (variety: RBL-6) was sown as a sequence in the end of April on residual soil fertility without disturbing the original layout of main crop. Crop management practices for buck wheat and ricebean are similar during both the year. All the organics, (well decomposed) were incorporated on dry weight basis 20 days before sowing of buck wheat. 20 days after application of organics as per treatment buck wheat were sown during 19th January and 21st January in 2012 and 2013, respectively with a seed rate of 40 kg ha-1. Improved agro techniques were followed for the crops. All the plants from individual plots were harvested at physiological maturity and data on agronomic parameters were recorded. Composite soil sample from each plot were collected after harvesting of both buck wheat and ricebean. The samples were systematically dried up in shade, pulverized, passed through 0.2 mm net and then determined for the available N, P and K. Standard statistical methods were used for comparing the treatment means. Treatments variations were analysed on the basis of F test results and critical differences were calculated at 5% level of probability. Economics was calculated based on the prevailing market price.

Results and Discussion

Stem Yield, Seed Yield and Harvest Index of Buckwheat

The seed and stem yield of buckwheat was, in general more in 2013 than in 2012 irrespective of organic sources for nutrient management (Table 1). Significantly, the highest stem (2.83 t ha-1 during 2012 and 2.97 t ha-1 during 2013) and seed yield (1.65 t ha-1 during 2012 and 1.77 t ha-1 during 2013) was observed in integrated  use of vermicompost at 2.5 t ha-1 + mustard cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 +  F.Y.M at 4 t ha-1 (T14) might be due to more leaf area, dry matter accumulation, crop growth and yield attributes followed by joint application of  vermicompost at 2.5 t ha-1 + mustard cake at 5 t ha-1 (T12) that was statistically equal with sole appliance of poultry manure at 5 t ha-1 (T8) during both the years of experimentation. The improvement of buckwheat yield due to different organic sources of nutrients could be attributed to the by and large advancement of crop growth, production and translocation of sufficient photosynthate. Unfertilized control (T1) recorded the lowest stem and seed yield of buck wheat during both the years of investigation. The results confirmed the experimental findings of Dietrych et al.,5, 6

It would further be seen from the said table that the highest harvest index (36.8 % and 37.3 %   during 2012 and 2013, respectively) was recorded under the collective  use of vermicompost at 2.5 t ha-1 + mustard cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 +  F.Y.M at 4 t ha-1  followed by joint use of  vermicompost at 2.5 t ha-1 + mustard cake at 5 t ha-1  (34.1 %  during 2012 and 35.2 %   during 2013) which was statistically equal with sole appliance of poultry manure at 5 t ha-1  (33.3 % and 34.9 %  during 2012 and 2013, respectively). Unfertilized control (T1) recorded significantly the lowest harvest index of 23.3 % and 25.3 % during 2012 and 2013, respectively.

Growth attributes and fodder yield of rice bean

Combine application of poultry manures, mustard cake and vermicompost to previous buckwheat crop significantly increased fodder yield of rice bean  by 40 and 45 q ha-1, during 2012 and 2013, respectively, over 100 % RDF (Table 2) might be due to higher residual fertility for greater nutrient uptake and availability. Similar significant increases on plant height (115.6 and 117.8 cm), number of branches plant-1 (5.2 and 5.3) and number of leaves plant-1 (77.7 and 78.3) were also observed in T14 followed by joint use of vermicompost at 2.5 t ha-1 + mustard cake at 5 t ha-1 (T12) which was statistically equal with the sole application of poultry manure at 5 t ha-1 (T8) during both the years of experimentation. As soil of terai region is sandy loam with light textured, prevailing with high rainfall, causes leaching down of nutrients, that’s why combined application of all the organic manures was added in treatment T14. All the treatments comprised organic sources of plant nutrient exhibited positive left over consequence in terms of yield traits and fodder yield of rice bean than chemically treated and control plot. Chemically treated plot left insufficient amount of nutrient for the succeeding crop as most of the nutrients was utilized by the preceding crop and some portion was lost from the soil as compared to organically amended plots, as a result performance of rice bean was not at par with the organically amended plots. These results are in accordance with the findings of Iqbal et.al.,7,8 & 9

Soil Nutrient Status

Results showed that available nutrient content of soil depleted after completion of crop sequence as compared to their initial level (before buckwheat). Collective application of vermicompost  at 2.5 t ha-1 + mustard cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 +  F.Y.M at 4 t ha-1 (T14) witnessed considerably highest values of available nitrogen (161.9 and 168.2 kg ha-1), phosphorus (26.2 and 34.3 kg ha-1 ) and potassium (124.0 and 127.5 kg ha-1) followed by vermicompost at 2.5 t ha-1 + mustard cake at 5 t ha-1 and mustard cake at 5 t ha-1 during both years of experimentation. Organically treated plots recorded higher values of available nitrogen, phosphorus and potassium than chemically treated plots during both the years of experimentation. The probable reason might be due to losses of nutrients from chemically treated plot. The available nitrogen was higher might be due to the fixation of atmospheric nitrogen by buckwheat. It was also found that whenever, poultry manure was applied either solely or combindly with other organic manures recorded maximum available potassium in both the years, it might be due to higher potassium content in poultry manure. The result of the present study is in agreement with the result of Singh et.al.,8, 9 & 10

Economics of buckwheat-rice bean sequence

The data on economics of buckwheat-ricebean cropping sequence in relation to organic manures and chemical fertilizers have been presented in Table 3 and 4. The economics analysis revealed that maximum gross return of ₹ 91500 and ₹ 97920 ha-1 were achieved with collective application of vermicompost at 2.5 t ha-1 + mustard cake at 2.5 t ha-1 + poultry manure at 2.5 t ha-1 + F.Y.M at 4 t ha-1 i.e. T14 closely followed by ₹81820 and ₹88300 ha-1 with vermicompost at 2.5 t ha-1 + mustard cake at 5 t ha-1 i.e. T12 during 2012 and 2013, respectively. Higher gross return was simply due to higher yield of both the crop in the sequence during both the years of experimentation. The results showed that all the organic treatments recorded higher gross returns as compared to chemically treated and control plots.

Among all treatments T8 (poultry manure at 5 t ha-1) registered the highest earnings to the tune of ₹51901 ha-1 in 2012 and ₹57941 ha-1 in 2013. This was next to T2 (₹44992 ha-1 in 2012 and ₹50351 ha-1 in 2013). The net returns were less in first year of experiment as compared to the second year simply due to lesser yield for buckwheat and ricebean in the first year. Among the organic manures mustard cake recoded comparatively lower net returns in both the years might be due to higher unit price (₹ 8.0 kg-1) of mustard cake. The highest benefit: cost ratio (2.33 and 2.59 during 2012 and 2013, respectively) was noticed in T2 (100 % RDF) followed by T10 (2.07 and 2.33 during 2012 and 2013, respectively). This was owing to the less cost incurred by these treatments. The results corroborate with the earlier findings of Panwar and Munda11 and Jaet et.al.,12

Table 1: Performances of buckwheat as influenced by organic sources of nutrient.

Treatments

Seed yield   (t ha-1)

Stem Yield (t ha-1)

Harvest index (%)

2012

2013

Mean

2012

2013

Mean

2012

2013

Mean

T1

0.37

0.48

0.43

1.20

1.41

1.31

23.3

25.3

24.3

T2

1.14

1.24

1.19

2.59

2.72

2.66

30.9

31.2

30.8

T3

1.00

1.11

1.06

2.54

2.68

2.61

28.2

29.3

28.7

T4

1.24

1.33

1.29

2.63

2.72

2.67

32.0

32.8

32.4

T5

1.13

1.23

1.18

2.60

2.70

2.65

30.2

31.2

30.7

T6

1.35

1.47

1.41

2.84

2.79

2.81

32.1

34.5

33.4

T7

1.12

1.22

1.17

2.59

2.69

2.64

30.1

31.1

30.6

T8

1.41

1.52

1.46

2.79

2.83

2.81

33.3

34.9

34.2

T9

1.17

1.26

1.22

2.57

2.76

2.66

31.1

31.3

31.2

T10

1.27

1.39

1.33

2.70

2.79

2.75

32.0

33.1

32.6

T11

1.39

1.48

1.43

2.82

2.79

2.80

32.1

34.8

33.7

T12

1.46

1.58

1.52

2.81

2.90

2.86

34.1

35.2

34.7

T13

1.31

1.42

1.36

2.76

2.78

2.77

32.1

33.7

32.9

T14

1.65

1.77

1.71

2.83

2.97

2.90

36.8

37.3

37.0

S.Em(±)

0.08

0.10

0.09

0.08

0.10

0.08

0.94

0.94

0.94

CD (P=0.05)

0.23

0.28

0.25

0.24

0.29

0.24

2.75

2.75

2.74

 

Table 2: Residual effect of organics on the performance of rice bean grown after buck wheat.

Treatments

Plant height (cm)

Number of branches  plant-1

Number leaves plant-1

Fodder yield (t ha-1)

2012

2013

Mean

2012

2013

Mean

2012

2013

Mean

2012

2013

Mean

T1

98.1

102.5

100.3

3.3

3.7

3.5

29.7

31.0

30.4

11.00 11.20 11.10

T2

113.2

105.3

109.3

3.6

4.2

3.9

40.3

52.4

46.4

12.20 13.00 12.60

T3

114.2

102.9

108.5

3.4

3.8

3.6

32.7

34.3

33.5

11.50 11.40 11.50

T4

113.4

123.1

118.3

3.9

4.2

4.1

48.3

55.3

51.8

13.10 14.00 13.60

T5

114.2

113.6

113.9

3.5

4.0

3.7

38.7

40.0

39.4

12.00 12.30 12.20

T6

102.4

115.7

109.1

4.2

4.6

4.4

57.7

61.4

59.5

14.10 14.70 14.40

T7

112.7

114.4

113.5

3.5

3.9

3.7

35.7

37.2

36.4

11.70 12.00 11.90

T8

110.2

115.5

112.9

4.2

4.8

4.5

67.6

72.0

69.8

14.50 15.40 15.00

T9

114.6

115.3

114.9

3.9

4.2

4.1

45.7

53.6

49.6

12.30 13.50 12.90

T10

100.3

128.3

114.3

4.1

4.5

4.3

54.8

56.6

55.7

13.60 14.20 13.90

T11

113.5

114.9

116.7

4.2

4.8

4.5

60.7

66.9

63.8

14.30 15.00 14.70

T12

112.3

115.7

114.2

5.0

5.0

5.0

73.3

75.3

74.3

14.70 15.50 15.10

T13

115.3

116.5

114.0

4.2

4.5

4.3

55.7

56.7

56.2

13.70 14.50 14.10

T14

115.6

117.8

115.9

5.2

5.3

5.2

77.7

78.3

78.0

15.00 15.70 15.40

S.Em(±)

6.75

7.31

7.01

0.156

0.15

0.147

2.76

2.96

2.82

0.76 0.84 0.93

CD (P=0.05)

19.74

21.35

20.48

0.456

0.438

0.431

8.06

8.66

8.24

2.23 2.47 2.73

 

Table 3: Impact of organic sources of nutrients on soil fertility after harvesting of rice bean.

Treatments

Available nitrogen

 (Kg ha-1)

Available phosphorus

 (Kg ha-1)

Available potassium

(Kg ha-1)

2012

2013

Mean

2012

2013

Mean

2012

2013

Mean

T1

80.1

91.1

85.6

7.40

11.2

9.30

21.1

22.6

21.9

T2

70.2

75.2

72.7

10.2

14.3

12.2

31.2

31.7

31.5

T3

68.1

73.9

71.0

5.00

8.20

6.60

33.4

39.3

36.4

T4

75.1

80.1

77.6

14.2

19.0

16.6

66.3

72.8

69.6

T5

102.6

105.1

103.9

11.3

16.3

13.8

87.9

95.5

91.7

T6

142.9

156.4

149.7

22.3

26.4

24.3

96.2

101.2

98.7

T7

80.1

80.2

80.2

24.3

26.4

25.3

98.1

104.7

101.4

T8

120.1

125.0

122.5

27.1

29.3

28.2

103.0

110.3

106.7

T9

73.1

75.3

74.2

7.30

12.2

9.70

39.9

43.7

41.8

T10

76.3

77.2

76.7

15.2

21.3

18.2

63.0

72.2

67.6

T11

113.1

118.1

115.6

14.3

20.6

17.4

108.1

115.7

111.9

T12

159.3

165.1

162.2

23.4

26.3

24.8

114.1

120.6

117.3

T13

68.1

70.1

69.1

7.40

14.2

10.8

40.9

44.2

42.6

T14

161.9

168.2

165.1

26.2

34.3

30.2

124.0

127.5

125.7

S.Em(±)

4.81

4.64

3.65

1.26

1.07

0.95

2.26

2.70

1.60

CD (P=0.05)

14.04

13.56

10.68

3.68

3.13

2.78

6.61

7.90

4.69

 

Table 4: Cost of production of buckwheat and ricebean as influenced by organic sources of nutrients.

Treatments cost

( ha-1)

General cost for buckwheat production   

 ( ha-1)

General cost for ricebean production ( ha-1)

Total cost of production (buckwheat + ricebean)

( ha-1)

Treatments

2012

2013

2012

2013

2012

2013

2012

2013

T1

15195

15195

2104

2104

17299

17299

T2

2029

2150

15195

15195

2104

2104

19328

19449

T3

1000

10000

15195

15195

2104

2104

27299

27299

T4

20000

20000

15195

15195

2104

2104

37299

37299

T5

20000

20000

15195

15195

2104

2104

37299

37299

T6

40000

40000

15195

15195

2104

2104

57299

57299

T7

5000

5000

15195

15195

2104

2104

22299

22299

T8

10000

10000

15195

15195

2104

2104

27299

27299

T9

8000

8000

15195

15195

2104

2104

25299

25299

T10

6029

6150

15195

15195

2104

2104

23328

23449

T11

30000

30000

15195

15195

2104

2104

47299

47299

T12

50000

50000

15195

15195

2104

2104

67299

67299

T13

14000

14000

15195

15195

2104

2104

31299

31299

T14

39000

39000

15195

15195

2104

2104

56299

56299

Input cost of urea, single super phosphate, muriate of potash, farm yard manure, vermicompost, poultry manure and mustard cake were 6,8,15,1,4,2 and 8kg-1 respectively.

Table 5: Economics of buckwheat-ricebean sequence as influenced by organic sources of nutrients.

Treatments

Return from buckwheat ( ha-1)

Return from rice bean( ha-1)

Gross return

( ha-1)

Net return ( ha-1)

Benefit: Cost ratio

2012

2013

2012

2013

2012

2013

2012

2013

2012

2013

T1

18500

24000

6600

6720

25100

30720

7801

13421

0.45

0.78

T2

57000

62000

7320

7800

64320

69800

44992

50351

2.33

2.59

T3

50000

55500

6900

6840

56900

62340

29601

35041

1.08

1.28

T4

62000

66500

7860

8400

69860

74900

32561

37601

0.87

1.01

T5

56500

61500

7200

7380

63700

68880

26401

31581

0.71

0.85

T6

67500

73500

8460

8820

75960

82320

18661

25021

0.33

0.44

T7

56000

61000

7020

7200

63020

68200

40721

45901

1.83

2.06

T8

70500

76000

8700

9240

79200

85240

51901

57941

1.90

2.12

T9

58500

63000

7380

8100

65880

71100

40581

45801

1.60

1.81

T10

63500

69500

8160

8520

71660

78020

48332

54571

2.07

2.33

T11

69500

74000

8580

9000

78080

83000

30781

35701

0.65

0.75

T12

73000

79000

8820

9300

81820

88300

14521

21001

0.22

0.31

T13

65500

71000

8220

8700

73720

79700

42421

48401

1.36

1.55

T14

82500

88500

9000

9420

91500

97920

35201

41621

0.63

0.74

Selling price of buck wheat and faba bean were ₹70 and 40 kg-1, respectively.

Acknowledgements

The authors are thankful to the Department of Agronomy, Uttar Banga Krishi Viswavidyalaya for the financial support and Directorate of Farm for all kinds of assistance throughout the experimentation.

Reference

  1. Palaniappan S.P. and Siddeswaran K., Proceedings of the XIII National Symposium on integrated input management for efficient crop production, Tamil Nadu Agriculture University, Coimbatore, India. 1994;41-53.
  2. Hegde D.M., Indian J.  Agron. 1998;34(4):635-638.
  3. Sharma U.C., Indian J. Agric. Sci. 1990;60(2):119-122.
  4. Arora R.K., Current Advances in Buckwheat Res. 1995;1(3):39-46.
  5. Dietrych S.D., Podolska, G.  and Maj, L., Fragmenta  Agronomica, 2008;25(1):101-109.
  6. Inamullah G., Hulamullah S., Muhammad A.,  Khan A.A.,  Shazma A. and Khan S.A., Sarhad J. Agric. 2012;28(2):171-178.
  7. Iqbal K., Tanveer A., Ali  A., Ayub M. and Tahir M., Pakisthan J. Bio. Sc. 1998;1(3):212-214.
  8. Singh B., Singh Y., Maskina M. S. and Meelu O.P., Nutrient Cycling in Agro ecosystems. 1996;47(3):243-250.
    CrossRef
  9. Agbede T.M., Ojeniyi S.O. and Adeyemo A.J., American Eurasian J. Sustainable Agric. 2008;2(1):72-77.
  10. Mohamed A.M., Alagesan A., Vaiyapuri  K., Pazhanivelan S. and Sathyamoorthi K., J. Agron. 6(1):183-187.
    CrossRef
  11. Panwar A.S. and  Munda G.C., Indian J. Agril. Sci. 2007;77(12):814-818.
  12. Jat  S. R., Shivran  A. C., Kuri B. R., Choudhary G. L., Prajapat K. and Golada S. L., Environ Ecology. 2013;31:(2):488-491.
scroll to top