首页> 外文期刊>Water, Air, and Soil Pollution >EFFECTS OF ACID ANION ADDITIONS (TRIFLUOROACETATE AND BROMIDE) ON SOIL SOLUTION CHEMISTRY OF A NORTHERN HARDWOOD FOREST SOIL
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EFFECTS OF ACID ANION ADDITIONS (TRIFLUOROACETATE AND BROMIDE) ON SOIL SOLUTION CHEMISTRY OF A NORTHERN HARDWOOD FOREST SOIL

机译:酸性阴离子(三氟乙酸酯和溴化物)对北方硬木森林土壤溶液化学性质的影响

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Experimental plots within the Hubbard Brook Experimental Forest, NH, were treated with sodium trifluoroacetate (TFA) and lithium bromide (Br), to study the impact of TFA alone and in the presence of increased anion concentrations (e.g. acid deposition) on the soil solution chemistry of a northern hardwood forest soil. Trifluoroacetate is a major atmospheric degradation product of replacement compounds of chlorofluorocarbons (CFC) and Br is widely used as a hydrologic tracer. Calculated drainage losses via soil water flow were less than 60/100 of inputs, added during the summer, and TFA and Br were temporarily retained in the soil until fall. The initial indication of an acid input of the treatments (HTFA, HBr) in the Bs2 horizon, which reflects stream water chemistry as well, was an increase of base cations in the soil solution, decreasing the soil's acid neutralizing capacity. Thereafter, trifluoroacetate and Br concentrations peaked after the peak in base cations, synchronous with peaks in H+ and A1 concentrations. Organic anions, nitrate and chloride played the major role in accompaning base cations out of the solum. Sulfate retention at soil adsorption sites was increased by the presence of TFA and Br, reducing its role as a mobile anion of base cations in this experiment. Relative retention of anions for the whole profile of this northern hardwood forest soil was estimated by correlation analyses and input-output balances in decreasing order on an equivalant basis; SO_4 > to TFA = Br ≥ C1> NO_3> organic anions. Recovery from acid additions were recorded within several weeks after the treatments were stopped. Evaluating the impact of added chemical compounds to soils must be considered within the context of 1inkages among element cycles and pools.
机译:用三氟乙酸钠(TFA)和溴化锂(Br)处理新罕布什尔州哈伯德布鲁克实验森林内的实验地块,以研究单独的三氟乙酸和在阴离子浓度增加(例如酸沉降)存在下对土壤溶液的影响北部阔叶林土壤的化学性质。三氟乙酸盐是氯氟烃(CFC)替代化合物的主要大气降解产物,Br被广泛用作水文示踪剂。在夏季,通过土壤水流计算得出的排水损失少于投入的60/100,TFA和Br暂时保留在土壤中直至秋天。 Bs2层中处理(HTFA,HBr)的酸输入的最初迹象也反映了溪流水的化学性质,这是土壤溶液中碱性阳离子的增加,降低了土壤的酸中和能力。此后,三氟乙酸盐和溴的浓度在碱性阳离子的峰值之后达到峰值,与H +和Al浓度的峰值同步。有机阴离子,硝酸根和氯离子在将碱阳离子从贫民窟中带走时起了主要作用。 TFA和Br的存在增加了硫酸盐在土壤吸附位处的保留,从而降低了其在本实验中作为碱性阳离子的可移动阴离子的作用。通过相关性分析和等价的基础上的投入产出平衡,按负序估算了北部硬木森林土壤整个剖面中阴离子的相对保留量; SO_4>到TFA = Br≥C1> NO_3>有机阴离子。在停止处理后的几周内记录了从添加酸中恢复的情况。必须在元素循环和池中的1种墨水的背景下,评估添加的化合物对土壤的影响。

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