Nitrogen-Inorganic Forms

R. Mulvaney
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引用次数: 1858

Abstract

Most soils contain inorganic nitrogen (N) in the form of ammonium (NHt) and nitrate (NO)"). Nitrite (NOz) also may be present, but the amount is usually too small to warrant its determination, except in cases where NHt or NHt-forming fertilizers are applied to neutral or alkaline soils. Several other forms of inorganic N have been proposed as intermediates during microbial transformations of N in soils, including hydroxylamine (NH20H), hyponitrous acid (H2N20 2), and nitramide (NH2N02), but these compounds are thermodynamically unstable and have not been detected in soil. Until the 1950s, inorganic N was believed to account for <2% of total soil N, on the assumption that NHt and NO)" are completely recovered by extracting soil with a neutral salt solution. The validity of this assumption was challenged by the finding that some soils contain NHt in a form that is not extracted by exchange with other cations (e.g., Rodrigues, 1954; Dhariwal & Stevenson, 1958; Stevenson & Dhariwal, 1959; Bremner & Harada, 1959; Bremner, 1959; Schachtschabel, 1960, 1961; Young, 1962), and by estimates that the proportion of soil N in this form can exceed 50% for some subsurface soils (Stevenson & Dhariwal, 1959; Young, 1962). In such cases, NHt is said to be fixed, and fixed NHt has subsequently been defined as the NHt in soil that cannot be replaced by a neutral potassium salt solution (SSSA, 1987), such as 1 or 2 M KCI or 0.5 M K2S04, in contrast to exchangeable NHt, which is extractable at room temperature with such a solution. Existing information indicates that fixed NHt occurs largely, if not entirely, between the layers of 2: I-type clay minerals, particularly vermiculite and illite (hydrous mica), and that fixation results from entrapment of NHt in ditrigonal voids in the exposed surfaces upon contraction of the clay lattice (Nommik & Vahtras, 1982). The term, nonexchangeable NHt, has been used by Bremner (1965) and Keeney and Nelson (1982) in previous editions of this publication as a more precise alternative to fixed NHt. The same term is used in the present treatment, with specific reference to NHt determined by the method described in "Determination of Nonexchangeable Ammonium," which involves digestion with an HF-HCI solution following treatment of the soil with alkaline KOBr to remove exchangeable NHt and labile organic-N compounds.
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Nitrogen-Inorganic形式
大多数土壤含有无机氮(N)以铵态氮(NHt)和硝态氮(NO)的形式。亚硝酸盐(NOz)也可能存在,但数量通常太小,无法保证其测定,除非在中性或碱性土壤中施用NHt或形成NHt的肥料。其他几种形式的无机氮被认为是土壤微生物转化氮的中间产物,包括羟胺(NH20H)、次亚硝酸(h2n2o)和硝酰胺(NH2N02),但这些化合物热力学不稳定,尚未在土壤中检测到。直到20世纪50年代,无机氮被认为占土壤总氮的2%以下,假设NHt和NO可以通过中性盐溶液提取土壤完全恢复。这一假设的有效性受到了一些发现的挑战,即某些土壤中含有一种不能通过与其他阳离子交换而提取的NHt(例如,Rodrigues, 1954;达里瓦尔和史蒂文森,1958;Stevenson & Dhariwal, 1959;Bremner & Harada, 1959;Bremner 1959;Schachtschabel, 1960, 1961;Young, 1962),据估计,在某些地下土壤中,这种形式的土壤氮的比例可能超过50% (Stevenson & Dhariwal, 1959;年轻,1962)。在这种情况下,NHt被认为是固定的,固定NHt随后被定义为土壤中不能被中性钾盐溶液替代的NHt (SSSA, 1987),如1或2 M KCI或0.5 M K2S04,与可交换的NHt相反,可在室温下用这种溶液提取。现有信息表明,固定的NHt大部分(如果不是全部)发生在2:i型粘土矿物层之间,特别是蛭石和伊立石(含水云母),固定是由于NHt在粘土晶格收缩后在暴露表面的双方空隙中被捕获(Nommik & Vahtras, 1982)。在本出版物的前几版中,Bremner(1965)和Keeney和Nelson(1982)使用了“不可交换NHt”一词,作为固定NHt的更精确替代。在目前的处理中使用了相同的术语,具体涉及通过“测定非交换性铵”中描述的方法测定NHt,该方法涉及在碱性KOBr处理土壤后用HF-HCI溶液消化以去除可交换的NHt和不稳定的有机n化合物。
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Nitrogen-Inorganic Forms Kaolin and Serpentine Group Minerals Chemistry of Redox Processes in Soils Intake Rate: Sprinkler Infiltrometer 3.6.1.1 Laboratory
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