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Ahmad M. S, Zargar M. Y, Wani M. A, Wani S. A. Kausar S. Soil Health Indicators of Rhizospheric Soils of Apple (Malus Domestica Borkh.) Variety Delicious in Himalayan Kashmir. Biosci Biotech Res Asia 2017;14(1).
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Soil Health Indicators of Rhizospheric Soils of apple (Malus Domestica Borkh.) Variety Delicious in Himalayan Kashmir

Malik Sajad Ahmad1, M. Y. Zargar2, Muneeb Ahmad Wani3, Sartaj Ahmad Wani4 and Shaheena Kausar4   

1Division of Basic Sciences and Humanities, Wadura, Sopore, Baramulla, 193201.

2Directorate of Research, SKUAST-K, Shalimar, Srinagar, 190025.

3Division of Floriculture and Landscape Architecture, SKUAST-K, Shalimar, Srinagar,190025.

4Division of NRM, SKUAST-K, Wadura, Sopore, Baramulla, 193201.

Corresponding Author E-mail: malik.sajadahmad@yahoo.com

DOI : http://dx.doi.org/10.13005/bbra/2462

ABSTRACT: Rhizospheric soils are rich sources of nutrients, enzymes, proteins, beneficial microbes responsible for sustainable growth of the plants. They supply principal elements to the plant and also promote microbial activity in the soil and improve its structure, aeration, and water holding capacity, which in turn improve the soil capabilities to respond to inputs. This discourse deals with the evaluation of thirty composite soil samples collected from different apple orchards of Baramulla district of Kashmir valley and analyzed for soil characteristics (organic carbon content, total available N, P, K, S; EC, pH, total viable bacterial, fungal and actinomycetes count) which in turn were used as chemical and microbial indicators of rhizospheric soil health of apple orchards in Himalayan Kashmir. It was observed that the soil characteristics were significantly correlated.

KEYWORDS: available N; composite soil sample; K; organic carbon; P; rhizosphere; S

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Ahmad M. S, Zargar M. Y, Wani M. A, Wani S. A. Kausar S. Soil Health Indicators of Rhizospheric Soils of Apple (Malus Domestica Borkh.) Variety Delicious in Himalayan Kashmir. Biosci Biotech Res Asia 2017;14(1).

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Ahmad M. S, Zargar M. Y, Wani M. A, Wani S. A. Kausar S. Soil Health Indicators of Rhizospheric Soils of Apple (Malus Domestica Borkh.) Variety Delicious in Himalayan Kashmir. Biosci Biotech Res Asia 2017;14(1). Available from: https://www.biotech-asia.org/?p=21590

Introduction

Soil is a renewable natural resource and there is a hidden microbial world of incredibly diverse nature below its surface. The underground environment of a plant is as important for the plant health as the above ground part which contains harmonious friendly microorganisms to normalize the soil health and put pathogenic organisms to stress conditions, thus extend the life span of a soil (Dar, 2010). Interactions among the rhizobacteria, present in rhizospheric soils and the roots of plants have been studied intensively (Kurkcuoglu et al., 2007; Ambrosini et al., 2012; Souza et al., 2013). Rhizobacteria colonize plant roots where they multiply and occupy all the ecological niches found on the roots at all the stages of plant growth (Antoun and Prevost, 2006). Some of the rhizobacteria play a key role in the natural nutrient cycles. Some species of rhizobacteria are capable of N2 fixation, some mobilizing phosphorus, potassium, and sulphur in accessible forms in the soils. There is a considerable population of P and K solubilizing bacteria in soil, particularly in rhizosphere (Sperberg, 1958). Silicate bacteria were found to dissolve potassium, silicon and aluminum from insoluble minerals (Aleksandrov et al., 1967). The phosphorus and potassium are made available to plants when the minerals are slowly weathered or solubilized (Bertsch and Thomas, 1985). Bacteria, fungi and actinomycetes in the rhizospheric soils of apple trees may be taken as microbial indicators of their health status. Successful identification of an elite microbial strain capable of forming PGPS (Plant Growth Promoting Substances), solubilizing phosphorus, potassium, zinc and other essential minerals quickly in large quantity can conserve our existing resources and avoid environmental pollution hazards caused by heavy application of chemical fertilizers. The chemical indicators of soil health include its reaction (pH), salinity (EC) and the nutrient ion concentration. All the parameters have a significant bearing on physical and biological health of soil and hence on the plant growth.

Keeping in view the adverse effects of agro-chemicals on the soil health of apple orchards and their effect on growth and yield of apple crop, an attempt through the present study was made to assess the biological wealth status of the soils under apple in Kashmir valley.

Materials and Methods

The present investigation was carried out at the Regional Research Station and Faculty of Agriculture, Sher-e-Kashmir University of Agricultural Sciences and Technology of Kashmir, Wadura Campus. Thirty rhizosphere soil samples of apple trees (var. delicious) were collected from thirty representative orchards of ten selected villages of Baramulla district of Jammu & Kashmir. The collected samples brought in sterilized zip-locked polythene bags to the laboratory were analyzed after due processing. Organic carbon was determined  by Walkley and Black’s wet oxidation method (Jackson, 1967), available nitrogen by Kjeldhal method (Subbaiah and Asija,1956), available phosphorus by Olsen’s method (Muhr et al., 1965), available potassium by flame photometer method (Stanford and English, 1949) and available sulphur by Chesnin and Yein method (1951). The electrical conductivity was determined by EC Bridge (Jackson, 1967) and the pH of the soil was measured by using a digital pH meter (Jackson, 1967). Bacterial, fungal and actinomycetes populations were also calculated by plate count method using colony counter.

Results and Discussion

Perusal of the data presented in Table 1 and  Table 2 revealed that organic carbon (OC) in the rhizospheric soil samples of apple trees ranged between 1.54% and 1.93% with the mean value of 1.80% and standard deviation of 0.10. Available nitrogen was 425.65 to 466.36 kg ha-1 with mean value of 445.68 kg ha-1 having standard deviation 10.67. Similarly available phosphorus ranged from 17.45 to 20.25 kg ha­-1 with the mean of 18.86 kg ha-1 having the standard deviation of 0.76. The available potassium ranged from 175.66 to 197.18 kg ha­-1 with mean value of 187.74 kg ha-1 with standard deviation of 5.38. The results are in conformation with the results found by Subash, and Tahir 2011. The upper limit for available sulphur was recorded as 28.17 kg ha-1 and the lower limit was 23.11 kg ha-1. The mean available sulphur content in the soil samples collected from Baramulla district was recorded as 26.09 kg ha-1 having standard deviation of 1.45. The electric conductivity (EC) of the soil samples were from 0.15 to 0.39 dS m-1 with mean value of 0.28 dS m-1 and standard deviation 0.08. The pH recorded of the collected samples was slightly acidic narrowly ranged from 6.3 to 6.6. The viable bacterial population per gram ranged between 77.16 x 106 and 86.38 x 106 with the mean value of 81.96 x 106. The viable fungal population per gram of soil sample ranged between 60.72 x104 and 60.72×104 with the mean value of 58.45×104. The viable actinomycetes ranged between 32.98 x105 and 29.58 x105 with the mean value of 31.11 x105.The results are in conformation with the results shown by Wani et al. 2015.

Table 1: Mean Characteristics of soil samples collected from district  Baramulla

S. No. Location Organic carbon (%) Available nitrogen (kg ha-1) Available phosphorus (kg ha-1) Available potassium (kg ha-1) Available sulphur    (kg ha-1) Electrical conductivity (dSm-1) pH Total viable bacteria
(x 106/g)
Total viable fungi (x 104/ g) Total viable actinomycetes (x 105/g)
1. Pattan 1.83 443.27 19.15 188.81 25.98 0.23 6.3 82.26 57.38 29.80
2. Delina 1.78 439.23 19.21 184.32 24.85 0.26 6.4 81.92 59.39 32.11
3. Sangrama 1.80 455.12 18.44 186.34 27.31 0.31 6.4 81.87 57.76 29.91
4. Patukha 1.83 443.53 18.80 188.73 26.19 0.39 6.3 82.20 57.34 29.87
5. Dangerpora 1.82 448.85 18.00 188.45 26.88 0.34 6.3 82.00 59.50 32.15
6. Bomai 1.83 440.50 19.06 188.62 25.03 0.35 6.3 77.16 57.23 29.90
7. Janbazpora 1.83 449.75 19.10 188.77 26.97 0.39 6.3 83.81 60.27 32.4
8. Hadipora 1.93 466.36 20.25 197.18 28.17 0.15 6.3 86.38 60.72 32.98
9. Wadoora 1.86 444.59 19.18 190.58 26.48 0.21 6.3 84.42 60.23 32.46
10. Watergam 1.54 425.65 17.45 175.66 23.11 0.21 6.6 77.62 54.71 29.58

Table 2: One-Sample Statistics of Baramulla District

  T Mean Standard Deviation Standard Error Mean 95% Confidence Interval of the  Difference
Lower Upper
Organic Carbon 56.379 1.8050 0.10124 0.03202 1.7326 1.8774
Available Nitrogen 102.451 445.6850 10.67002 3.37416 338.0521 353.3179
Available Phosphorus 78.132 18.8640 0.76349 0.24144 18.3178 19.4102
Available Potassium 110.201 187.7460 5.38750 1.70368 183.8920 191.6000
Available Sulphur 56.905 26.0970 1.45023 0.45860 25.0596 27.1344
EC 10.731 0.2840 0.08369 0.02647 0.2241 0.3439
pH 206.626 6.3500 0.09718 0.03073 6.2805 6.4195
Viable Bacteria ( x 106) 92.252 81.9640 2.80960 0.88847 79.9541 83.9739
Viable Fungi (x 104) 98.107 58.4530 1.88411 0.59581 57.1052 59.8008
Viable Actinomycetes (x 105) 70.437 31.1160 1.39696 0.44176 30.1167 32.1153

With the increase in the pH the availability of organic carbon, available phosphorus, potassium and sulphur decreased significantly. At 95% to 99% confidence interval, Organic Carbon, available nitrogen, available phosphorus, available potassium and available sulphur showed positive significant correlation with each other except between available phosphorus and available sulphur (Table 3). These results are in conformity with the results of Sofi et al. 2012. The viable bacterial and fungal population in the rhizosphere of apple showed statistical positive significance with each other and with organic carbon, available nitrogen, phosphorus, potassium and sulphur.

Table 3: Correlations of soil characteristics of Baramulla district

  Organic Carbon Available Nitrogen Available Phosphorus Available Potassium Available Sulphur EC pH Bacteria Fungi Actinomy-cetes
Organic Carbon 1
Available Nitrogen 0.808** 1
Available Phosphorus 0.808** 0.642* 1
Available Potassium 0.966** 0.851** 0.824** 1
Available Sulphur 0.835** 0.958** 0.557 0.850** 1
EC 0.075 -0.079 -0.272 -0.069 0.054 1
pH -0.932** -0.612 -0.647* -0.872** -0.709* -0.301 1
Viable Bacteria 0.695* 0.765** 0.652* 0.732* 0.812** -0.266 -0.536 1
Viable Fungi 0.774** 0.715* 0.669* 0.752* 0.744* -0.062 -0.667* 0.826** 1
Viable Actinomycetes 0.509 0.527 0.512 0.540 0.523 -0.226 -0.394 0.732* 0.922** 1

**Correlation is significant at the 0.01 level,
*Correlation is significant at the 0.05 level.

Soil is a dynamic ecosystem that harbours many micro-organisms which are closely related to the plants. Microorganisms play their role in two ways one as pathogens causing diseases and the other as beneficial ones such as biological control agents and nutrient mobilizers and solubilizers. Numerous microorganisms, particularly those associated with roots, have the ability to increase plant growth and productivity (Chung et al., 2005). However, certain groups of microorganisms can directly or indirectly transform rocks and minerals in quantities large enough to influence the geological distributions. These transformations include enzymatic oxidation-reduction reactions, formation of chelates and complexes with protein, amino-acids, organic acids etc. (Henderson and Duff, 1963).

Conclusion

The following conclusion could be drawn from the present investigation. The distribution of microorganisms like bacteria and fungi in the rhizospheric soils of apple play a variety of roles in the growth and yield quality of apple by release of organic carbon; nitrogen fixation; solubilization of phosphorus, potassium, sulphur; plant growth promotion; and alleviation of stress which are statistically significantly correlated with essential macronutrients available in the rhizosphere.  So conserving the microbial activity in the soil is very important for release of essential nutrients in the rhizosphere for plant uptake and sustainable growth of the trees which are important indicators of soil health status.

Acknowledgements

The authors are thankful to the Hon’ble Vice Chancellor and Director Research, Sher-e-Kashmir University of Agricultural Sciences & Technology of Kashmir for providing research facilities.

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