Rogozhina Ye. V.

All Russia Scientific and Research Institute of Floriculture and Subtropical Crops, Sochi, Russia, e-mail: RogojinaEW@yandex.ru

Influence of fertilizers on nitrogen-fixing activity of brown forest acid soil in a tea plantation of subtropical Russia

         We studied the potential nitrogen-fixing activity of brown forest acid soils of tea plantation under the influence of fertilizers in the conditions of the Black Sea coast of Russia. In general, nitrogen-fixing activity (AA) of soils was characterized by low values and ranged from 0.37 to 2.1 ng C2H4 / (g h). Adding fertilizers in medium (N200P60K50 kg / ha of active substance) and the highest (N600P180K150 kg / ha of active substance) doses inhibited the nitrogen-fixing ability of brown forest acid soil of tea plantation.

         Keywords: tea plant, the potential nitrogen-fixing activity, fertilizers, subtropical zone of Russia.

         Brown forest acidic soil of moist subtropics of Russia of natural biocenoses (beech and hornbeam forest) are characterized by low supply of available forms of nitrogen (30 - 50 mg/kg) [5], so the cultivation of agriculture, especially tea (Camellia sinensis), requires the use of high doses of nitrogen fertilizers.

         One of the criteria used for monitoring the microbial succession in the soil under the influence of fertilizers and determination of the level of agrogenic load is the study of the intensity of the nitrogen fixation process. The process of nitrogen fixation is influenced by a complex of various factors: acidity, humidity, soil temperature, the presence of mobile forms of nitrogen, the composition of the microbial community and the relationship of microorganisms, fertilizers. As a result, nitrogen-fixing capacity of soils varies depending on the vegetation period plants, agrocenosis, agricultural practices of cultivation [8]. In experiments of in vitro has been long ago established the influence of inhibition of nitrogen fixation in the presence of free forms of nitrogen in the environment, but the question of its impact on nitrogen fixation in the soil in the presence of the plants is still complex and poorly studied [7].

         In this regard, the aim of this study was to explore the features of the effect of different doses of fertilizers on nitrogen-fixing ability of potential brown forest acid soil in the conditions of agro-ecosystems of tea in subtropical zone of Russia.

         We studied the nitrogen-fixing activity (AA) of brown forest acidic soils of beech and hornbeam forests (background) and three varieties of the experimental sections of many years tea plantation of Kolkhida sort the coastal strip of the Big Sochi (Uch-Dere). Exploring options differed in doses of applied mineral fertilizers: control - N0P0K0 (without fertilizers); single - doses N200P60K50 kg / ha of active substance; triple doses - N600P180K150 kg / ha of active substance. The size of experimental plots - 50m2. Fertilizers by the experimental scheme were brought in according to the zonal Guidelines: 60% of nitrogen and 100% of phosphate and potash fertilizers in April, 40% of nitrogen - in June, in the form of dressing. The mixed soil samples were taken in August and October 2008, from the topsoil (0 -10cm) in compliance with the rules of sterility.

         Potential nitrogen fixation was determined by the method of acetylene reduction on a Kristall-2000 gas chromatograph with flame ionization detector and a column length of 1 m, column diameter of 3 mm, filling of Porapak N 80/100, column temperature of 60°C, detector temperature of 160°C, vaporizer temperature of 100°C, carrier gas flow (N2) of 50 ml/min, air flow of 280 ml/min, and hydrogen flow of 28 ml/min. The activity of nitrogen fixation was expressed in ng of C2H4/(g h) [6]. Agrochemical characteristics were determined by methods widely used in the practice of agrochemical analysis [1]: pHsal was determined potentiometrically in a suspension with a soil : KCl solution ratio of 1 : 2.5 (ionometer pH-121); the humus content was determined according to the method of Turin in the modification of Orlov and Grindel’; the content of mobile forms of phosphor and potassium it was determined according to Oniani; easily hydrolyzed nitrogen was determined according to Turin and Kononova using the colorimetric method with the Nessler reagent, colorimeter KFK-3 (wave length 400–440 nm); and humidity was determined by the weight method.

         The temperature of air and soil in August - +240C and +180C, in October - +170C and +130C, respectively. Soil moisture during this period varied slightly (August average of 36.5%, in October - 34.8%), which was due to sufficient rainfall in August. The acidity of the samples varied in the range of 3.06 to 4.2 (Fig. 1).

Fig.1. The acidity of the soil experimental tea plantation

         According to the established gradations, these soils were characterized by low (N0P0K0, N200P60K50) and medium (forest, N600P180K150) humus content (average of 3.3 and 5.5%, respectively); hydrolysable nitrogen content varied from low values (forest, N0P0K0) to high (N600P180K150) (from 53 to 187 mg/kg, respectively); provision of mobile phosphorus - from low (N0P0K0) to high (N600P180K150) (from 108 to 1200 mg/kg, respectively); potassium content is high (from 464 to 478 (mg/kg) [4].

         The studies found that the of brown forest acidic soils of beech and hornbeam forests (background) in the summer-autumn period were characterized by low values of the potential nitrogen-fixing activity(AA) (Fig. 2) and were comparable with the values obtained for the brown earth of the southern taiga forests(pHH2O= 4.6) [2]. This fact was due to the high acidity of the soil solution which inhibits the nitrogenase activity of free nitrogen fixers [3; 7].

         AA soil agrophytocenosis of tea (without fertilizer) had values close to the background. Adding fertilizers in medium (N200P60K50), and in high doses (N600P180K150) inhibited the nitrogen-fixing ability of brown forest acid soil of tea plantation (Fig. 2).

Fig. 2 Potential nitrogen-fixing activity (AA) influence of fertilizers in a tea plantation

         The decrease in the AA control values (N0P0K0) under the influence of the fertilizer is more pronounced in October (2.4 times) compared to August (1.3 times). This correlated with the acidity (Fig. 1) that we have previously noted (r = - 0.74) [8].

         With the reduction the acidity of the soil in October, the decrease of AA during the fall was determined, apparently, by the soil temperature, to a lesser extent by humidity.

         Thus, minor differences of nitrogen-fixing capacity of the soils of natural cenosis (beech and hornbeam forest) and agrocenosis of tea plantation (without mineral fertilizers) were set at this stage. The application of mineral fertilizers in the studied doses inhibited the nitrogen-fixing ability of brown forest acid soil of tea plantation.

REFERENCES

1.                 Agrokhimicheskie metody issledovaniya pochv(Agrochemical Methods for Soils Investigation), Moscow: Nauka, 1975.

2.                 Grishakina, I.E., Trofimov, S.Ya., Stepanov, A.L., and Dorofeeva, E.I., Microbial Transformation of Nitrogen Compounds in Soils of the Southern Taiga, Pochvoved., 2006, no. 11 [Eur. Soil Sci. (Engl. Transl.), 2006, vol. 39, no. 11, p. 1233].

3.                 Daraseliya, N.A., Biologicheskaya aktivnost’ osnovnykh pochv Zapadnoi Gruzii (Biological Activity of Western Georgia Basic Soils), Tbilisi: Metsiereba, 1979.

4.                 Malyukova, L.S., Sistema udobreniya plantatsii chaya v subtropicah Rossii (The system of fertilizer tea plantations in subtropics Russia) / L. S. Malyukova, N. V. Kozlova, Z. V. Prytula - Sochi: GNUVNIITsiSK, 2010. - 45 s.

5.                 Malyukova, L.S., Kozlova, N.V., Strukova, D.V., and Rogozhina, E.V., The Ways to Implement the Scientific Principals for Generating the Stable Agroecological Systems in Subtropical Agriculture, in Bioresursy, biotekhnologii, ekologicheski bezopasnoe razvitie agropromyshlennogo kompleksa (Bioresources, Biotechnologies, Ecologically Friendly Development of Agricultural Sector), Sochi, 2007.

6.                  Mineev, V.G., Praktikum po agrokhimii (Practical Work on Agricultural Chemistry), Moscow: MGU, 2001.

7.                 Umarov, M.M., Kurakov, A.V., and Stepanov, A.L., Mikrobiologicheskaya transformatsiya azota v pochve (Microbiological Nitrogen Transformation in the Soil), Moscow: GEOS, 2007.

8.                 Rogozhina E.V. Estimation of Ðotential Nitrogen-Fixing Activity of Agrophytocenoses Soils of the Subtropical Zone of Russia / Ye.V. Rogozhina, N.V. Kostina, L.S. Malyukova // Moscow University Soil Science Bulletin, 2011. Vol. 66, ¹ 1. pp. 32-35.