THE USE OF COMPOST TO REDUCE LEAKAGE OF MINERAL NITROGEN LYSIMETER EXPERIMENT

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THE USE OF COMPOST TO REDUCE LEAKAGE OF MINERAL NITROGEN LYSIMETER EXPERIMENT Plošek L., Elbl J., Jaroslav Z. Department of Agrochemistry, Soil Science, Microbiology and Plant Nutrition, Faculty of Agronomy, Mendel University in Brno, Zemedelska 1, 613 00 Brno, Czech Republic E-mail: lukas.plosek@mendelu.cz ABSTRACT This paper presents first results from long term pot experiment, which is focused on influence of addition of compost on leaching of mineral nitrogen. Twenty one lysimeters were prepared in the area of our interest. This area is a protection zone of underground source of drinking water (Březová nad Svitavou). These lysimeters were filed with topsoil and subsoil collected in this area and divided into two groups. The content of mineral nitrogen was measured in soil solution (percolate), which was collected from each lysimeters. First results confirm the hypothesis that the addition of organic carbon (in form of compost) has positive effect on mineral nitrogen leaching. The highest leaching of mineral nitrogen was measured in variant with 100 % of N addition and the lowest in the variant with the 200 % addition of compost. Key words: compost, leaching of mineral nitrogen, lysimeter, nitrogen Acknowledgments: The work was supported by the National Agency for Agricultural Research (NAZV), project: The possibilities for retention of reactive nitrogen from agriculture in the most vulnerable infiltration area of water resources, registration no.: QJ 1220007. 347 P age

INTRODUCTION Application of compost in agriculture is very desirable worldwide. In the Czech Republic, compost is the most often used to improve soil structure and increase the content of soil organic matter, but the effects of compost addition on the fate of mineral nitrogen are only scarcely described (ELBL et al. 2013, PLOŠEK et al. 2013). The largest part of global nitrogen pollution stems from agricultural activities (GALLOWAY et al. 2003). Reduction of fertilizing is not satisfactory to prevent losses of mineral nitrogen from agricultural systems (TAMM 1991). It will be necessary to change the method of farming. One option is to support the microbial activity in humus horizon (rhizosphere). Microbial activity can be supported by the addition of carbon (SUTTON 2011). Microbial processes supported by added carbon increase the capacity of the soil for capturing of mineral nitrogen. Nitrogen is subsequently stored in soil organic matter. The deposited organic nitrogen can be used later by plants or soil microorganisms and cannot be easily lost from arable land (DIAZ et al. 2007, SUTTON 2011). Leaching of mineral nitrogen (consisting of NH 4 + -N and NO 3 - -N) from arable land is a major threat to the quality of drinking water from underground reservoirs in the Czech Republic [9]. In the present paper, effect of compost addition on leaching of mineral nitrogen from arable land was investigated in field lysimetric experiment. MATERIAL AND METHODS Experimental design Influence of compost addition on mineral nitrogen leaching was tested by pot experiment. Twenty one lysimeters have been used as experimental containers and located in the area. The experiment was conducted in the protection zone of underground source of drinking water Březová nad Svitavou, where annual climatic averages (1962-2012) are 588.47 mm of precipitation and 7.9 C mean of annual air temperature (ELBL et al. 2013). The lysimeters were made from PVC (polyvinyl chloride). Each lysimeter was the same size and was filled with 25 kg of subsoil and 25 kg of topsoil (arable soil). See Figure 1. Fig. 1: Design of experimental container - lysimeter (ELBL et al. 2013) 348 P age

Topsoil and subsoil were collected from a field in the area. Soil samples were sieved through a sieve (grid size of 10 mm) and homogenized. Topsoil and subsoil were prepared separately. Each lysimeter had one drain hole and PVC hose for collecting soil solution. Hose leads into the plastic bottle. All lysimeters were buried into the ground. Collection of soil solution and monitoring of the lysimeters was carried out in the control shaft. Lysimeters were completed and filled in October 2012. Winter wheat (Triticum aestivum) was used as a model plant to determine the effect of fertilizers and on plant production. The model crop was planted into each lysimeter in October 2012. Seven variants (C1, C2 and K1 - K5) were prepared: C1 (control - without fertilization), C2 (control - with 100 % of recommended doses of N), K1 (100 % of recommended doses of compost), K2 (100 % of compost, 25 % of N), K3 (100 % compost, 50 % of N), K4 (100 % of compost, 100 % of N), K5 (200 % of compost). Information on the applied fertilizers: Compost was applied in recommended doses of 50 Mg/ha from Central composting plant in Brno (Compost Černý drak). Nitrogen was applied as a liquid fertilizer DAM 390 converted in dose of 140 kg/ha of N. Determination of mineral nitrogen Soil solution was collected into plastic bottles, which were placed in the control shaft. The amount of the solution was monitored three times per week. If a solution was found in a bottle, it was taken for the determination. Samples were stored at 4 C before the determination. Concentration of mineral nitrogen (N min ) was measured using distillation-titration method by (PEOPLES et al. 1989). Ammonium nitrogen was determined by distillation-titration method in an alkaline solution after the addition of MgO. Nitrate nitrogen was determined in the same manner using Devard s alloy. Concentration of NH + 4 -N and NO - 3 -N was calculated: mg NH 4 + or NO 3 N = normality of standart HCl 0,03571 x 0,5, xtitration (BROOKES et al. 1985) The value of N min was calculated as the sum of the detected ammonium and nitrate forms. Determination of N min was performed after each sampling of the soil solution and in each sample. The results obtained from the analyses of soil solution were expressed in mg of N min per m 2 (mg/m 2 ). RESULT AND DISCUSSION Leaching of mineral nitrogen From January to July 2013, the concentration of mineral nitrogen (N min ) was measured in soil solution. The solution was captured from individual lysimeters. The Figure 2 shows concentration of N min in individual variants. This graph indicates a significant difference (P<0.05) in content of N min before and after application of fertilizers in soil solution. 349 P age

Fig. 2: Concentration of N min n soil solution (mean ± SD, n = 3) The highest concentration of N min was measured in variant with 100 % of recommended doses of N (C2 = 367 mg N/m 2 ) and the lowest in the variant with 200 % doses of compost (K5 =117 mg N/m 2 ). Reduce leakage of mineral nitrogen in variants with the addition of compost can be explained by the addition of available organic carbon (Corg) in the form of compost. The possotive effect of Corg on soil microbial activity and decreasing of mineral nitrogen leaching confirm for example Elbl et al. (2013), Plošek et al. (2013) and Sutton (2011). CONCLUSIONS This contribution presents the first results of a long-term pot experiment. The measured values indicate the influence of addition of compost and mineral nitrogen fertilizer on leaching of mineral nitrogen. Based on the results, that the high addition of compost has positive effect on leaching of mineral nitrogen. REFERENCES P. C. Brookes, A. Landman, G. Pruden and D. S. Jenkinson, Chloroform fumigation and the release of soil nitrogen: A rapid direct extraction method to measure microbial biomass nitrogen in soil, Soil Biology and Biochemistry, vol. 17, no. 6, 1985. L. F. Diaz, M. de Bertoldi, W. Bidlingmaier, E. Stentiford, Compost science and technology. Boston: MA Elsevier, 2007, cha. 3. J. Elbl, L. Plošek, A. Kintl, J. Přichystalová, J. Záhora and J. Hynšt, Effect of organic-waste compost addition on leaching of mineral nitrogen from arable land and plant production, World Academy of Science, Engineering and Technology, no. 78, pp. 2858-2863, 2013. J. N. Galloway, J. D. Aber, J. W. Erisman, S. P. Seittzinger, R. W. Howarth, E. B. Cowling, B. J. Cosby. The Nitrogen cascade, BioScience, vol. 53, no. 4, pp. 341-356, 2003. A. Kintl, J. Hynšt, J. Zahora, J. Elbl, L. Plosek, L. Halada, I. Tůma, F. Kohút, Contrasting effect of nitrogen and phosphorus addition on soil microbial activities at alpine meadow, in Proceedings of International Masaryk conference for Ph.D. students and young researchers, Hradec Králové, 2012, pp. 3693-3702. 350 P age

L. Plošek, J. Elbl, A. Kintl, J. Záhora, J. Hyšt, Vliv přídavku kompostu na únik minerálního dusíku a produkci biomasy, Waste Forum, vol. 2013 no. 1, pp. 20-28. M. A. Sutton, The European nitrogen assessment: sources, effects and policy perspectives. New York: Cambridge University Press, 2011, cha. 1, 5. C. O. Tamm, Nitrogen in terrestrial ecosystems: Questions of productivity, vegetational changes and ecosystem stability, Berlin: Springer Verlag, 1991. 351 P age