You are here

Biological activity of podzolized chernozem after prolonged application of fertilizers in the field crop rotation

Biological activity is one of the indicators of soil fertility which shows regularities in processes of organic matter transformation and determines intensity of biochemical activity of soil microorganisms. The research aims at studying the effect of long-term application (45 years) of different doses of fertilizers and fertilizer systems in the field crop rotation on the intensity of carbon dioxide emissions, cellulosolytic activity and nitrification capacity of the soil. The research was conducted in a long-term, stationary experiment, based on the ten-course crop rotation. Fertilizers are applied using the mineral system (N45P45K45; N90P90K90; N135P135K135), the organic system (Manure 9 t; 13.5 t; 18 t) and the organic-mineral fertilizer system (Manure 4.5 t + N22P34K18; Manure 9 t + N45P68K36; Manure 13.5 t + N68P101K54). Doses of fertilizers are given for 1 hectare of the crop rotation. The soil of the experimental field is loamy podzolized chernozem.

According to the results of studies, it is found out that prolonged use of mineral fertilizers in the field crop rotation provided the intensity of carbon dioxide emissions from the soil surface at the level of 181–217 mg/m2 per hour. The use of a double dose of mineral fertilizers (N90P90K90) increased the biological activity of the soil compared to non-fertilized areas by 23 %. Regarding the corresponding doses of organic fertilizer system (applying 18 tons of manure for 1 hectare) and organic-mineral one (application of 9 t/ha of manure + N45P68K36), when N90P90K90 is applied the intensity of CO2 emissions from the soil surface was less than 20 % and 22 %, respectively. Regarding the influence of organic fertilizers in the field crop rotation on the biological activity of the soil, it should be noted that carbon dioxide emissions were more intensive and varied within the limits of 209–256 mg/m2 per hour that is more compared to non-fertilized areas by 1.3–1.5 times depending on the dose of fertilizer. The highest intensity of CO2 emissions from the soil surface was observed in the variant with the application of 18 tons of manure for 1 hectare that is more by 25 % than in N90P90K90 variant.

Combined application of organic and mineral fertilizers in the field crop rotation provided the highest intensity of carbon dioxide emissions (222–279 mg/m2 per hour) depending on the fertilization and was close to CO2 emissions from the grassland. Application of 9 tons of manure + N45P68K36 for 1 hectare increased the intensity of CO2 emissions from the soil by 28 % compared to N90P90K90 variant and by 2 % in the variant of manure of 18 tons.

The largest amount of carbon dioxide was from the grassland and amounted to 286 mg/m2 per hour. A slightly lower intensity of CO2 emission was from the soil under the tree belt area (268 mg/m2 per hour). The least carbon dioxide emissions were from the soil surface of unfertilized areas (166 mg/m2 per hour).

The greatest intensity of flax decomposition in 30 days was observed using mineral and organic and mineral fertilizer systems among all experimental variants after prolonged use of different doses of fertilizers and fertilizer systems in the field crop rotation. Application of the mineral fertilizer system in the field crop rotation provided cellulosolytic activity of the soil at the level of 54–68 % which is more than in the variant without fertilizers, respectively, by 29–62 %.

Combined application of organic and mineral fertilizers in the field crop rotation provided the intensity of flax decomposition in the range of 51–66 % depending on fertilizer doses which is more compared with the organic fertilizer system, respectively, by 4–35 %. A slightly lower soil cellulosolytic activity was observed in the organic fertilizer system (49–62 %) which is explained by lower nitrogen yield due to organic fertilizers.

Due to the low humus content in the soil, the intensity of flax decomposition dramatically slows down. As a result, the low value of cellulosolytic activity in the soil without fertilizer is 42 % which is less compared with the variant in which the application is 13.5 tons of manure + N68P101K54 by 36 %, respectively.

Accumulation of nitrates in the soil during composting without impurities depends on the doses of fertilizers and fertilizer systems. Thus, there was 17.7 mg of N–NO3/kg of soil after composting soil from unfertilized areas in 14 days. The highest accumulation of nitrate nitrogen was observed at high doses of fertilizers: in the mineral fertilizer system it was 1.5 times more, in the organic fertilizer system it was by 1.7 times and in the organic and mineral one it was 2.1 times compared with the check variant.

More accumulation of nitrates was during composting soil with the addition of ammonium sulfate. Thus, in the soil without fertilization, the content of nitrate nitrogen increased 3.6 times and its value was 63.9 mg of N–NO3/kg. After composting soil with the addition of (NH4)2SO4, the accumulation of nitrates was directly proportional to the level of fertilization. In variants with application of N45P45K45, 9t of manure and 4.5 tons of manure + N23P34K18 there was 72.4 mg of N–NO3/kg, 79.8 and 81.5 mg of N–NO3/kg of soil. After high doses of fertilizers its amount increased to 85.7 mg N–NO3/kg, 99.9 and 115.7 mg N–NO3/kg in accordance with the experimental variant.

Composting soil with the addition of ammonium sulfate in combination with lime is the best way to discover the potential of the nitrification process. The obtained data testify that calcium application into the soil positively affects the activity of microbiological processes. At the same time, lime neutralizes the physiologically acidic action of the fertilizer, as well as nitrates formed during the composting process which thereby enhances the activity of nitrifying agents. In the soil of unfertilized areas, after composting with (NH4)2SO4 + CaCO3, the nitrate content increased from 17.7 mg of N–NO3/kg to 89.3 mg of N–NO3/kg. In variants with the use of fertilizers their accumulation also increased in accordance with the level of fertilization. Thus, in variants with application of N135P135K135, 18 t of manure and 13.5 t of manure + N68P101K54, there were
148.2 mg of N–NO3/kg, 176.0 and 196.3 mg of N–NO3/kg of soil, respectively.

Key words: biological activity of the soil, mineral fertilizers, manure, field crop rotation, podzolized chernozem, soil fertility.

 

Reference: 

1. Furdychko, O.I. (2014). Ahroekolohiya [Agroecology]. Kyiv, Agrarian science, 400 р.

2. Pavlichenko, A.A., Bondarenko, O.M., Vakhniy, S.P. (2015). Zmina biolohichnoyi aktyvnosti gruntu pid vyko-vivsyanoyu sumishkoyu za riznykh system obrobitku gruntu ta rivniv udobrennya [Changing biological activity of the soil using the vetch and oat mixture after different soil tillage systems and fertilization levels]. Ahrobiolohiya [Agrobiology], no. 1, pp. 31–34.

3. Volkohon, V.V., Tokmakova, L.M., Volkohon, K.I., Dehodyuk, S.E., Kovpak, P.V., Trepach, A.O., Larchenko, I.V., Ty-moshenko, O.P., Lepekha, O.P., Zhurba, M.A., Lytvynova, N.V. (2015). Mikrobiolohichni aspekty produktsiynoho protsesu silʹsʹkohospodarsʹkykh kulʹtur za orhanichnoyi systemy zemlerobstva: naukovo-praktychni rekomendatsiyi [Microbiological aspects of the production process of agricultural crops in the organic system: scientific and practical recommendations]. Chernihiv, 39 p.

4. Tsylyuryk, O.I., Kulik, A.F., Honchar, N.V. (2017). Biolohichna aktyvnistʹ gruntu za riznykh sposobiv yoho obrobitku ta udobrennya v posivakh sonyashnyku [Biological activity of soil after different methods of its cultivation and fertilization in sunflower crops]. Visnyk Dnipropetrovsʹkoho derzhavnoho ahrarno-ekonomichnoho universytetu: naukovo-teoretychnyy, naukovo-praktychnyy zhurnal [Bulletin of Dnipropetrovsk State Agrarian and Economic University: Scientific-Theoretical, Scientific-Practical Journal], no. 2 (44), pp. 42–48.

5. Volkohon, V.V., Zaryshnyak, A.S., Pylypenko, L.A., Dimova, S.B., Volkohon, K.I., Zhurba, M.A., Shtanʹko, N.P., Lutsenko, N.V. (2015). Obgruntuvannya ekolohichnoyi dotsilʹnosti system udobrennya silʹsʹkohospodarsʹkykh kulʹtur za pokaznykamy biolohichnoyi transformatsiyi azotu v grunti [Substantiation of ecological expediency of fertilizer systems of agricultural crops by indicators of biological transformation of nitrogen in the soil]. Kyiv, 39 p.

6. Zinchenko, M.K., Bibik, T.S., Stoyanova, L.G. Infl uence of systems of fertilizers on structure and change of separate physiological groups of microorganisms in grey forest pochve Vladimirsky opolya. Fundamental research. 2014, no. 12, pp. 552–557.

7. Russell, E.J. Soil conditions and plant growth. Forgotten Books. London, 2013, 406 p.

8. Natywa, M., Selwet, M., Maciejewski, T. Wpływ wybranych czynników agrotechnicznych na liczebność i aktywność drobnoustrojów glebowych. Fragmenta Agronomica. 2014, no. 31, pp. 56–63.

9. Dubytsʹka, A.O., Kachmar, O.Y., Dubytsʹkyy, O.L., Shcherba, M.M. (2014). Vplyv system udobrennya na biolohichnu aktyvnistʹ siroho lisovoho gruntu pid ozymoyu pshenytseyu v lankakh sivozmin [Influence of fertilizer systems on the biological activity of gray forest soil under winter wheat in crop rotations]. Peredhirne ta hirsʹke zemlerobstvo i tvarynnytstvo [Foothill and mountain farming and livestock production], Issue 56 (1), pp. 38–42.

10. Pavlichenko, A.A., Bondarenko, O.M., Vakhniy, S.P. (2014). Vplyv system obrobitku ta rivniv udobrennya na yoho biolohichnu aktyvnistʹ pid ozymoyu pshenytseyu [Influence of cultivating systems and fertilization levels on the soil biological activity for winter wheat]. Ahrobiolohiya [Agrobiology], no. 2, pp. 131–134.

11. Purtova, L.N., Kostenkov, N.M., Semal', V.A., Komachkova, I.V. (2013). Emissiya uglekislogo gaza iz pochv prirodnykh i antropogennykh landshaftov yuga Primor'ya [Carbon dioxide emission from soils of natural and anthropogenic landscapes of the Seaside south]. Fundamental'nyye issledovaniya [Fundamental research], Issue 3, no. 1, pp. 585–589.

12. Patyka, M.V., Moskalevsʹka, Yu.P. (2014). Mikrobiolohichni protsesy transformatsiyi vuhletsyu v ryzosferi buryaka tsukrovoho chornozemu typovoho [Microbiological processes of carbon transformation in rhizosphere of sugar beets in the typical chernozem]. Visnyk Poltavsʹkoyi derzhavnoyi ahrarnoyi akademiyi [Bulletin of Poltava State Agrarian Academy], no. 2, pp. 34–39.

13. Volkohon, V.V., Zhurba, M.A. (2013). Aktyvnistʹ azotfiksatsiyi, emisiya N2O ta CO2 v ahrotsenozakh horokhu za diyi dobryv i peredposivnoyi bakteryzatsiyi [Nitrogen fixation activity, emissions of N2O and CO2 in peas agrocenoses under the influence of fertilizers and pre-sowing bacteritization]. Silʹsʹkohospodarsʹka mikrobiolohiya [Agricultural microbiology], Issue 18, pp. 16–29.

14. Zhurba, M.A., Volkogon, K.I. (2015). Biological denitrification in the soils of agrocenoses upon combination of microbial preparations whith nitrogen fertilizers. Microbiological aspects of optimizing the production process of cultured crops. Chernihiv, 2015, pp. 23–24.

15. Kovalenko, A.M., Kuts, H.M. (2015). Zroshennya i sivozminy yak faktor vplyvu na mikrofloru gruntu [Irrigation and crop rotations as a factor of influence on the soil microflora]. Materialy Vseukrayinsʹkoyi naukovo-praktychnoyi konferentsiyi «Evolyutsiya gruntiv Ukrayiny pid vplyvom antropohennoyi diyalʹnosti» [Materials of the All-Ukrainian Scientific and Practical Conference «Evolution of soils of Ukraine under the influence of anthropogenic activity»]. Kherson, Issue 9, pp. 29‒34.

16. Rybacki, M., Polkowska, M., Piotrowska-Długosz, A. Przydatność testów enzymatycznych do oceny wpływu nawożenia naturalno-mineralnego na aktywność biologiczną gleby. Ekologia i Technika. 2014, no. 22, pp. 248–255.

17. Lykhovyd, P.V., Lavrenko, S.O. Influence of tillage and mineral fertilizers on soil biological activity under sweet corn crops. Ukrainian Journal of Ecology. 2017,  no. 7 (4), pp. 18–24.

18. Bhattacharya, A., Sahu, S.K., Hundet, A., Sarkar, P. Effect of urea, superphosphate, potash and npk on soil respiration (carbon dioxide evolution from soil). Indian Streams Research Journal Available. 2013, no. 3 (10), pp. 1–10.

19. Geisseler, D., Scow, K.M. Long-term effects of mineral fertilizers on soil microorganisms – A review. Soil Biology and Biochemistry. 2014, Vol. 75, pp. 54–63.

20. Naher, U.A., Radziah, O., Panhwar, Q.A. Culturable total and benefi cial microbial occurrences in long-term nutrient defi cit wetland rice soil. Australian Journal of Crop Science. 2013, no. 7 (12), pp. 1848–1853.

21. Pavlichenko, A.A., Vakhniy, S.P. (2013). Vplyv system obrobitku ta rivniv udobrennya na biolohichnu aktyvnistʹ gruntu pid yachmenem [Influence of cultivating systems and fertilization levels on the soil biological activity for barley]. Ahrobiolohiya [Agrobiology], no. 11 (104), pp. 136–138.

22. Kovalʹov, V.B., Trembitsʹka, O.I., Radʹko, T.V. (2015). Biolohichna aktyvnistʹ gruntu za orhanichnoyi systemy vyroshchuvannya kulʹtur u korotkorotatsiyniy sivozmini [The soil biological activity in the organic system of growing crops in short crop rotation]. Ahropromyslove vyrobnytstvo Polissya [Agricultural and industrial production of Polissia], Issue 8, pp. 15–20.

23. Rusakova, I.V. (2013). Biologicheskiye svoystva dernovo-podzolistoy supeschanoy pochvy pri dlitel'nom ispol'zovanii solomy na udobreniye [Biological properties of sod-podzolic sandy loam soil with long-term use of straw as a fertilizer]. Pochvovedeniye [Soil Science], no. 12, pp. 1485–1493.

24. Chen, Ll., Gu, J., Hu, T., Gao, H., Chen, Z.X., Qin, Q.J., Wang, X.J. Effects of biological organic fertilizer on microbial community’s metabolic activity in a soil planted with chestnut (Castanea mollissima). Ying Yong Sheng Tai Xue Bao. 2013, no. 24 (6), pp. 1627–32.

25. Malynovsʹka, I.M., Dehodyuk, S.E., Yastremsʹka, L.S. Vplyv orhanichnoho i mineralʹnoho udobrennya na chyselʹnistʹ ta fizioloho-biokhimichnu aktyvnistʹ mikroorhanizmiv siroho lisovoho gruntu [Influence of organic and mineral fertilizers on number and physiological-biochemical activity of microorganisms of the gray forest soil]. Problemy ekolohichnoyi biotekhnolohiyi [Problems of environmental biotechnology], 2017, no. 2. Retrieved from: http://ecobio.nau.edu.ua/index.php/ ecobiotech/article/view/12194/16294.

26. Demʹyanyuk, O.S., Sherstoboyeva, O.V., Demydov, O.A. (2016). Biolohichna aktyvnistʹ chornozemu typovoho zalezhno vid vydu orhanichnoho substratu orhano-mineralʹnoyi systemy udobrennya [Biological activity of typical chernozem depending on the type of organic substrate of the organic and mineral fertilizer system]. Visnyk Zhytomyrsʹkoho natsionalʹnoho ahroekolohichnoho universytetu [Bulletin of Zhytomyr National Agroecological University], no. 2 (1), pp. 17–25.

27. Piaszczyk, W., Błońska, E., Lasota, Ja. Study on the effect of organic fertilizers on soil organic matter and enzyme activities of soil in forest nursery. Soil science annual. 2017, Vol. 68, no. 3, pp. 125–131.

28. Błońska, E., Januszek, K., Małek, S., Wanic, T. Effects of serpentinite fertilizer on the chemical properties and enzyme activity of young spruce soils. International Agophysics. 2016, no. 30 (4), pp. 401–414.

29. Dębska, B., Długosz, J., Piotrowska-Długosz, A., Banach-Szott, M. The impact of a bio-fertilizer on the soil organic matter status and carbon sequestration-results from a field-scale study. Journal of Soils and Sediments. 2016, no. 16, pp. 2335–2343.

30. Kosolapova, A., Yamaltdinova, V., Mitrofanova,  E., Fomin, D. Biological activity of soil depending on fertilizer systems. Bulg. J. Agric. Sci. 2016, no. 22 (6), pp. 921–926.

31. Lazcano, C., Gómez-Brandón, M., Revilla, P., Domínguez, J. Short-term effects of organic and inorganic fertilizers on soil microbial community structure and function. Biol. Fertil. Soils. 2013, no. 49 (6), pp. 723–733.

32. Snitynsʹkyy, V.V., Habryyelʹ, A.Y., Hermanovych, O.M., Olifir, Yu.M. (2014). Biolohichna aktyvnistʹ yasno-siroho lisovoho poverkhnevo-ohleyenoho gruntu zalezhno vid antropohennoho vplyvu [Biological activity of gray forest gleyed soil depending on anthropogenic impact]. Silʹsʹkohospodarsʹka mikrobiolohiya [Agricultural microbiology], Issue 19, pp. 47–52.

33. Shtatnov, V.I. (1952). K metodike opredeleniya biologicheskoy aktivnosti pochvy [Methods for determining the biological activity of soil]. Doklady VASKHNIL [Reports by the A-UAASNL], Issue 6, pp. 27–33.

34. Mishustin, Ye.N., Petrova, A.I. (1963). Opredeleniye biologicheskoy aktivnosti pochvy [Determination of the soil biological activity]. Mikrobiologiya [Microbiology], Vol. 22, Issue 3, pp. 473–483.

35. Lisoval, A.P., Davydenko, U.M., Moyseyenko, B.M. (1994). Ahrokhimiya [Agrochemistry]. Kyiv, High school, 335 p.

 

Download this article: 
AttachmentSize
PDF icon trus-agro-1-2018-106-115.pdf267.62 KB