A Brief Description of Spatial Analysis and Superimposing of Essential Elements in Pomegranate Using GIS Technique

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Journal of the Indian Society of Soil Science, Vol. 66, No. 2, pp 144-148 (2018) DOI: 10.5958/0974-0228.2018.00018.X A Brief Description of Spatial Analysis and Superimposing of Essential Elements in Pomegranate Using GIS Technique H.B. Raghupathi*, S. Srinivas and V.M. Shilpashree Indian Institute of Horticultural Research, Hessaraghatta Lake Post, Bangalore, 560 089, Karnataka Spatial variability of soil properties and accompanying variability in plant nutrient concentration in a pomegranate growing enterprise was mapped using GIS technique. About 23 acre land in a farmer s field was selected and intensively sampled on a regular grid spacing of 21 m. Geo-statistical analysis was used to describe the spatial variability. The geo-statistical procedure of Kriging was used for interpolation of grid data to understand spatial correlation between neighbouring observations and to prepare contour maps. Among the essential elements studied, the available Mg in soil showed a good relationship with plant Mg, while for all other elements, the relationship between soil and plant nutrients was very poor. The variogram models of soil properties indicated that most of the properties exhibited definable spatial structures. ph, available N, Ca, Mg, Fe, Mn and Zn showed strong spatial dependence, whereas available P, K and S showed moderate spatial dependence. Most of the plant nutrients exhibited high nugget : sill ratio indicating often mismatch between soil available nutrient and plant nutrient concentration. The extent to which the spatial variability of soil available nutrient mimicked that of plant nutrient status was a function of nutrient element in question. Application of GIS for nutrient mapping was found useful for developing nutrient management strategies in pomegranate. Key words: GIS technique, spatial analysis, soil and plant nutrient status, pomegranate The nutrient requirement for perennial fruit crops like pomegranate (Punica granatum) through soil testing is done by comparing the soil available nutrient status with established ranges for soil under question. Alternately, the mineral composition in selected plant samples in pomegranate leaf provides insight on nutrient requirement. Conventionally, one or a few samples are collected within the field for assessment of nutrient requirement. However, when soil sampling approach is adopted, the spatial variability in soil properties poses problem for sampling and diagnosis of nutrient requirement. When plant sampling approach is adopted the nutrient interactions within the plant vitiates the diagnosis of nutrient imbalance (Fageria 2001). To overcome this problem, grid sampling has been widely used for understanding spatial and temporal variations as it provides excellent information about intrinsic and management induced *Corresponding author (Email: Raghupathi.HB@icar.gov.in) Present address 1 National Bureau of Soil Survey and Land Use Planning, Regional Centre, Agricultural Farm Post, Hebbal, Bangalore, 560024, Karnataka variations within the field (Balasundram et al. 2008). Grid sampling helps in GIS application which envisages application of geo-statistics to describe the spatial variability. The basic objective is to generate information on unknown locations/points which is not sampled when limited samples are collected within a field. The geo-statistical procedure of Kriging is applied for interpolation of grid data to understand spatial correlation between neighboring observations and to prepare smooth contour maps. The spatial dependence between two neighboring samples is explained by semi-variance. As the distance between the two samples increases as the variance increases (Kirandeep et al. 2011). Pomegranate is an important fruit crop in India and nutrient management is one of the most challenging production constraints. Notwithstanding, many progressive farmers are making use of soil and plant analysis facilities for improving yield potential. The present investigation was taken up to find the spatial variability in a pomegranate growing enterprise and to establish relationship between soil available nutrients and plant nutrient status by preparing

2018] SPATIAL ANALYSIS AND SUPERIMPOSING OF ESSENTIAL ELEMENTS IN POMEGRANATE 145 nutrient contour maps. This article shows how diverse soil properties can be integrated to make soil and plant analysis more meaningful for fertilizer recommendation by making use of data generated locally in a pomegranate orchard. Material and Methods Grid sampling Twenty three acres of land in a farmer s field in Ballalasamudra of Hosadurga was demarcated and intensively sampled on a regular grid spacing of 21 m. The four geo-coordinates of the farm were roughly identified using global positioning system (GPS) operator. Surface soil samples (0-15 cm) were collected from 140 grid points. Soil samples were analyzed for different nutrients in order to develop nutrient contour maps. A composite leaf sample from four to six plants surrounding each grid point was collected. The 8 th pair of leaf from the top was collected (Anonymous 2004). The relief within the study plot was less than 1 m. Analysis of samples Soil samples were analyzed for ph, electrical conductivity (EC), organic carbon (OC), available N, P, K, Ca, Mg, S, Fe, Mn and Zn by following standard procedures (Page et al. 1982). The plant samples were analyzed for N, P, K, Ca, Mg, S, Fe, Mn, Zn and Cu as outlined by Jones et al. (1991). The foliar samples were dried at 65 C, wet digested with H 2 SO 4 and H 2 O 2 and analyzed for N by Kjeldahl method. Another part of the sample was digested with HNO 3 : HClO 4 (9: 4, v/v) and P was estimated by vanadomolybdate method and S by turbidimetric method. Atomic 214 m absorption spectrophotometer was used for determining Ca, Mg, Fe, Mn, Zn and Cu. Potassium was estimated using flame photometer. Geo-statistics Geo-statistical analysis was used to describe the spatial variability. Sampling grids were digitized as polygons using GIS software. The geo-statistical procedure of Kriging was used for interpolation of grid data to understand spatial correlation between neighboring observations and to prepare contour maps. The results of the soil and plant analysis were used in descriptive statistical analysis by calculating mean, median, minimum and maximum values, skewness and kurtosis. The spatial dependence was analyzed by semi-variogram based on the accepted stationarity assumptions which constitute intrinsic hypothesis of regional variable theory (Webster 1985). The geo-statistical parameters were derived by placing grid values in XY coordinates. where, S 2 is the semi-variance for 'm' pairs of observations and Z(x i ) and Z (x i + h) are observations separated by the distance 'h' usually known as lag. The coefficients of the semi-variogram theoretical model viz., nugget effect, range sill were estimated. The degree of spatial dependence of the properties under study was interpreted by the classification of Cambardella et al. (1994), which considers strong spatial dependence of semi-variogram with nugget: sill ratio <25%, moderate when the ratio is between 25 and 75% and poor when the ratio is >75%. Results and Discussion 109 m 163 m Fig. 1. Grid sampling in pomegranate 318 m Soil properties Soil reaction varied form near neutral to acidic, while for most of the samples EC was in the safe range. Organic carbon content was moderate and N was marginally low. Both P and K were in optimum range in most of the samples. The DTPA extractable Fe, Mn and Cu were in optimum range when compared to the established ranges, whereas mean Zn was marginally low in few samples (Table 1). Such large variations in soil properties within a small area is not uncommon and other studies evaluating spatial variations found similar variation in soil properties within a localized area (Kirandeep et al. 2011).

146 JOURNAL OF THE INDIAN SOCIETY OF SOIL SCIENCE [Vol. 66 Table 1. Soil available nutrients in pomegranate orchards under grid sampling Mean Min Max ph 5.42 4.16 7.76 EC (ds m -1 ) 0.28 0.10 0.83 OC (%) 0.51 0.20 1.72 N (ppm) 82.6 32.1 278 P (ppm) 8.39 2.14 33.9 K (ppm) 184 77.5 350 Ca (ppm) 2548 709 5357 Mg (ppm) 214 56.5 363 S (ppm) 53.1 10 165 Fe (ppm) 15.7 7.98 33 Mn (ppm) 28.6 6.75 68.2 Zn (ppm) 1.21 0.48 18.4 Cu (ppm) 1.88 0.83 5.90 Plant nutrient status The mean N, P and K concentration in pomegranate leaf sample were 2.43, 0.26 and 1.48%, respectively. Phosphorus concentration in leaf was not yield limiting factor and in many cases, had marginally higher P in leaf and nearly all most all the samples had P greater than established critical value of 0.18% (Anonymous 2004). All the samples were in optimum range with reference to K when compared to the established standard (>0.61%). Calcium concentration showed wide range and was generally high ranging from 0.59 to 4.83%, while Mg concentration was in optimum range in majority of samples compared to norms developed elsewhere. Iron concentration was higher than the optimum range developed earlier and it varied widely from 85 to 355 Table 2. Nutrient concentration in grid-sampled pomegranate leaf samples Mean Min Max N (%) 2.43 0.32 3.93 P (%) 0.26 0.01 0.60 K (%) 1.48 0.90 3.60 Ca (%) 2.26 0.59 4.83 Mg (%) 0.65 0.36 1.08 S (%) 0.29 0.16 0.49 Fe (ppm) 208 85.5 355 Mn (ppm) 110 33.6 277 Zn (ppm) 39.2 13.4 175 Cu (ppm) 26.2 10.8 58.1 ppm (Table 2). Both Zn and Cu concentration was in general on the higher range. Boron concentration showed wide variation in leaf ranging from 5.3 to 30.5 ppm. Nutrient contour maps Although array of soil and plant nutrients were mapped, only the N distribution in soil and plant system is illustrated for sake brevity. Application of variogram models indicated that most of the properties exhibited definable spatial structure although the models they subscribed to were different for each element and were either linear with sill, exponential or Gaussian. Among different soil parameters some were spatially dependent and some were spatially independent. Nitrogen distribution followed stable model both in soil and plant (Fig 2). The distribution of available N in soil was patchy and there was region of high N (a) (b) Distance (x axis) vs Semi-variance (y axis) Fig. 2. Schematic representation of nitrogen semi-variogram model for soil (a) and plant (b)

2018] SPATIAL ANALYSIS AND SUPERIMPOSING OF ESSENTIAL ELEMENTS IN POMEGRANATE 147 Table 3. Assessment of the status of soil and plant nutrients in pomegranate orchard and geo-statistical summary Variant Soil Plant Nugget (Plant) Sill (Plant) Superimposing N Optimum High 0.316 0.418 No Agreement P Optimum High 0.0053 0.023 Poor Agreement K Optimum Optimum 0.087 0.024 No agreement Ca High High 0.28 0.08 Partial agreement Mg Optimum Optimum 0.009 0.002 Good agreement S High Optimum 0.002 0.004 Poor agreement Fe Optimum Optimum 1805 651 Poor agreement Mn Optimum Optimum 0.001 1396 Poor agreement Zn Optimum Optimum 514 74 Poor agreement Cu optimum Optimum 30.75 49.09 Poor agreement Fig. 3. Nitrogen contour maps for plant and soil on one side of the farm and plants growing nearby did not show similar high N in leaf samples. The nugget:sill ratio for soil was (236.3%) and was higher when compared to nugget:sill for plant (75.6%) indicating that N levels in plant showed much higher spatial dependence compared to soil N. Nitrogen concentration in plant showed a poor relationship with available N in soil. This is primarily because of poor microbial activity of arid region soil and therefore low uptake by plant. Figure 3 indicates several vital facts regarding N management in pomegranate taken as an example. There was a patch of land where N was very low in soil and therefore higher level of N application is required than the recommended value. However, it is to be observed that the N levels in soil was not reflected in plant as one can make out visually superimposing soil and plant contour maps. Literature is replete with information on poor relationship between soil available N and leaf N concentration in pomegranate (Raghupathi et al. 2002) notwithstanding adequate N in soil. The K concentration variation in soil and plant also showed poor correlation and often were not related. In general, the K concentration in soil was higher while majority of the area in plant showed a very low K content. Phosphorus distribution within the orchard showed far greater spatial dependence (nugget: sill ratio 23.0), whereas K exhibited very poor spatial dependence. Similarly, some of the micronutrients like Fe and Zn also showed poor spatial dependence. Among the 10 nutrient elements studied, element by element comparison indicated that only Mg showed very good agreement between soil and plant status. The nugget: sill ratio value for a given element was more often lower for plant compared to the ratio for soil indicating that plant nutrient was spatially more dependable when compared to soil available nutrient levels. None of the micronutrients showed agreement between soil and plant status with reference to spatial variability. This was partly because of poor mobility of micronutrients within plant and also due to existence of interaction within plant with other nutrients (Fageria 2001). Conclusions Spatial analysis through GIS application was instrumental in establishing relationship between available nutrients in soil and its concentration in plant in pomegranate. Understanding nutrient behaviour in soil and plant is important as illustrated above. However, the GIS application can be extended to soil physical, chemical and even to biological

148 JOURNAL OF THE INDIAN SOCIETY OF SOIL SCIENCE [Vol. 66 properties and integrate them effectively. The optimum ranges have been developed for pomegranate both soil parameter and plant nutrient status earlier, however often the interpretation based on such comparison was too vague. Nutrient application has been taken up based on annual demand of the crops rather than spatial demand. The study indicated that understanding the spatial variability across the same study site provided means estimating nutrient requirement from management perspective. References Anonymous (2004) Leaf analysis in fruit crops. Extension Folder No 45-07, Indian Institute of Horticultural Research Hessaraghatta, Bangalore, India. Balasundram, S.K., Husni, M.H.A. and Ahmed, O.H. (2008) Application of geo-statistical tools to quantify spatial variability of selected soil chemical properties from a cultivated tropical peat. Journal of Agronomy 7, 82-87. Cambardella, C.A., Moorman, T.B., Novak, J.M., Parkin, T.B., Karlen, D.L., Turco, R.F. and Konopka, A.E. (1994) Field scale variability of soil properties in central Iowa soils. Soil Science Society of America Journal 58, 1501-1511. Fageria, V.D. (2001) Nutrient interaction in crop plants. Journal of Plant Nutrition 24, 1269-1290. Jones Jr, J.B., Wolf, B. and Mills, H.A. (1991) Plant Analysis: Handbook - A Practical Sampling, Preparation, Analysis and Interpretation Guide. Micro-Macro Publishing Inc., Athens, USA, pp. 1-213. Kirandeep, K.M., Arnold, W.S., Thomas, A., Max, O.T., Willie, G.H. and Jerry, B.S. (2011) Spatial variability of soil chemical and biological properties in Florida citrus production. Soil Science Society of America Journal 75, 1863-1873. Page, A.L., Miller, R.H. and Keeny, D.R. (1982) Methods of Soil Analysis. Part 2 Am Soc Agron Inc. Madison USA, pp. 403-430. Raghupathi, H.B., Reddy, B.M.C. and Srinivas, K. (2002) Multivariate diagnosis of nutrient imbalance in pomegranate. Communications in Soil Science and Plant Analysis 33, 2143-2143. Webster, R. (1985) Quantitative spatial analysis of soil in the field. In Advances in Soil Science 3, 2-66. Revised received 28 October 2017; Accepted 16 May 2018