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首页> 外文期刊>Biology and Fertility of Soils >Mineralization-immobilization of soil organic S and oxidation of elemental S in subtropical soils under flooded and nonflooded conditions
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Mineralization-immobilization of soil organic S and oxidation of elemental S in subtropical soils under flooded and nonflooded conditions

机译:在淹没和非淹没条件下亚热带土壤中有机硅的矿化固定和元素S的氧化

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Information on the influence of soil moisture on elemental sulphur (S0) oxidation and transformation into organic S in semi-arid subtropical soils is scarce. We studied the impact of three moisture regimes on the mineralization of soil organic S, and the oxidation and immobilization of S0 in acidic (pH 4.9), neutral (pH 7.1) and alkaline (pH 10.2) subtropical soils. Repacked soil cores were incubated under aerobic (40% and 60% water-filled pore space, WFPS) and flooded soil conditions (120% WFPS) for 0, 14, 28 and 42 days with and without incorporated S0 (500 µg g–1 soil). Soil moisture had profound effects on these processes and the mineralization of native soil organic S, oxidation of applied S0 and transformation of S0 into soil organic S proceeded most rapidly at 60% WFPS, irrespective of soil pH. Mineralization of native soil organic S resulted in the accumulation of 34, 49 and 44 g SO4 2–-S g–1 soil in acidic, neutral and alkaline soil in a 42-day period at 60% WFPS. The oxidation rate of added S0 during the initial 14-day period at 60% WFPS was highest in alkaline soil (428 µg S cm–2 day–1), followed by neutral soil (326 µg S cm–2 day–1), and lowest in acidic soil (235 µg S cm–2 day–1). These rates are several folds higher than those reported in earlier studies because now we computed the oxidation rates by including the amount of S0 that was immobilized to organic S. Of the applied S0 at 40% and 60% WFPS, 2.6% and 6.0%, 3.4% and 10.0%, and 9.4% and 14.4% oxidized to SO4 2–, and 15.0% and 17.6%, 17.6% and 19.6%, and 17.6% and 23.6% transformed into organic S in the 42-day period in acidic, neutral and alkaline soil, respectively. These results suggest that in order to synchronize the availability of S with plant need, S0 may be applied well before the seeding of crops especially in acidic soils and in rainfed regions where soil moisture remains at less than 60% WFPS. Apparently no oxidation of S0 and significant reduction of SO4 2–-S (7, 53 and 78 µg SO4 2–-S g–1 in acidic, neutral and alkaline soil, respectively) under flooded conditions suggest that S0 is least effective for correcting S deficiency in flooded soil systems such as rice fields.
机译:关于半干旱亚热带土壤中土壤水分对元素硫(S0 )氧化和转化为有机S的影响的信息很少。我们研究了三种水分制度对土壤有机S矿化以及在酸性(pH 4.9),中性(pH 7.1)和碱性(pH 10.2)亚热带土壤中SO的氧化和固定化的影响。将重新包装的土壤核心在有氧和未掺入S0的情况下,在有氧(40%和60%充满水的孔隙空间,WFPS)和水淹条件(120%WFPS)下孵育0、14、28和42天(500微克g–1 土壤)。土壤水分对这些过程有深远的影响,无论土壤pH值如何,在60%WFPS下,天然土壤有机S的矿化,施用的S0 的氧化以及S0 转化为土壤有机S的过程最为迅速。原生土壤有机S的矿化作用导致42、42和49 g SO4 2 – -S g–1 土壤在42天的酸性,中性和碱性土壤中积累期间的WFPS为60%。在最初的14天中,以60%WFPS的添加S0 的氧化速率在碱性土壤中最高(428 µg S cm–2 day–1 ),其次是中性土壤(326 µg S cm–2 day–1 ),在酸性土壤中最低(235 µg S cm–2 day–1 )。这些比率比早期研究中报道的比率高出几倍,因为现在我们通过包括固定在有机S上的S0 的量来计算氧化率。在所施加的S0 中分别为40%和60% WFPS分别氧化为SO4 2-的2.6%和6.0%,3.4%和10.0%,9.4%和14.4%,以及15.0%和17.6%,17.6%和19.6%和17.6%在酸性,中性和碱性土壤中,分别有42.5%和23.6%的化合物在42天内转化为有机硫。这些结果表明,为了使S的可用性与植物需求同步,可以在作物播种之前很好地施用SO,特别是在酸性土壤和土壤湿度保持低于60%WFPS的雨育地区。显然没有S0 的氧化并且SO4 2- -S(7、53和78 µg SO4 2- -S g-1 < / sup>分别在酸性,中性和碱性土壤中)在淹没条件下进行,这表明S0 对纠正稻田等淹没土壤系统中的S缺乏效果最差。

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