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Nitrate reductase activity of soils
Institution:2. College of Agriculture, SKRAU, Bikaner, India;3. Bihar Agricultural University, Bhagalpur, India;4. Department of Soil Science and Agricultural Chemistry, Institute of Agricultural Sciences, Banaras Hindu University, Varanasi, India;1. Department of Environmental Health Engineering, Maragheh University of Medical Sciences, Maragheh, Iran;2. Health and Environment Research Center, Tabriz University of Medical Sciences, Tabriz 5166614711, Iran;3. Department of Environmental Health Engineering, Abadan University of Medical Sciences, Abadan, Iran;4. Department of Environmental Health Engineering, School of Public Health, Shahid Beheshti University of Medical Sciences, Tehran, Iran
Abstract:Dissimilatory nitrate reductase in soils is the enzyme that catalyzes the reduction of NO33 to NO2 under anaerobic conditions. The detection of this enzyme in soils is reported, and a simple, sensitive and precise method to assay its activity is described. The method involves determination of the NO2-N produced when soil. 2,4-dinitrophenol (DNP), and KNO3 are incubated under waterlogged conditions at 25°C for 24 h. At a certain concentration, depending on the soil type, DNP inhibits nitrite reductase but not nitrate reductase. The DNP concentration required for optimum NO2 production in five soils ranged from 5 to 300 μg DNP g−1 soil. The nitrate reductase activity of six soils studied ranged from 18 to 80 μg NO2-N produced g−1 soil 24 h−1. Optimum activity was found at 5 mM KNO3 and nitrate reductase was inhibited at >5 mM KNO3. Nitrate reductase activity in soils is inactivated at temperatures above 40°C and is completely destroyed by steam sterilization. The relationship between duration of incubation and the amount of NO2-N produced showed a lag of about 10 h, but in general, thereafter, this relationship was linear for a certain period of incubation, which varied among the soils studied. The duration of the lag was reduced, but not completely eliminated, either by previous incubation for 10 h or by bubbling N2 gas in the soil-water mixture for 3 min to remove the dissolved O2 in the soil-water mixture before addition of NO3. The relationship between the amount of soil used and the NO2-N produced was linear unless the substrate concentration was limiting the reaction rate. Application of the Lineweaver-Burk transformation of the Michaelis-Menten equation indicated that the Km values for nitrate reductase in Ames and Okoboji soils were 3.7 and 2.9, respectively, and the Vmax values were 122 and 126μg NO2-N produced g soil 24 h.
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