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纽约奥奈达湖锰的生物地球化学循环:锰的全湖研究

Biogeochemical cycling of manganese in Oneida Lake, New York: whole lake studies of manganese.

作者信息

Aguilar C, Nealson K H

机构信息

Great Lakes Water Institute, University of Wisconsin-Milwaukee 53204, USA.

出版信息

J Great Lakes Res. 1998;24(1):93-104. doi: 10.1016/s0380-1330(98)70802-0.

Abstract

Oneida Lake, New York is a eutrophic freshwater lake known for its abundant manganese nodules and a dynamic manganese cycle. Temporal and spatial distribution of soluble and particulate manganese in the water column of the lake were analyzed over a 3-year period and correlated with other variables such as oxygen, pH, and temperature. Only data from 1988 are shown. Manganese is removed from the water column in the spring via conversion to particulate form and deposited in the bottom sediments. This removal is due to biological factors, as the lake Eh/pH conditions alone can not account for the oxidation of the soluble manganese Mn(II). During the summer months the manganese from microbial reduction moves from the sediments to the water column. In periods of stratification the soluble Mn(II) builds up to concentrations of 20 micromoles or more in the bottom waters. When mixing occurs, the soluble Mn(II) is rapidly removed via oxidation. This cycle occurs more than once during the summer, with each manganese atom probably being used several times for the oxidation of organic carbon. At the end of the fall, whole lake concentrations of manganese stabilize, and remain at about 1 micromole until the following summer, when the cycle begins again. Inputs and outflows from the lake indicate that the active Mn cycle is primarily internal, with a small accumulation each year into ferromanganese nodules located in the oxic zones of the lake.

摘要

纽约的奥奈达湖是一个富营养化的淡水湖,以其丰富的锰结核和活跃的锰循环而闻名。在3年的时间里,对该湖水柱中可溶性和颗粒态锰的时空分布进行了分析,并将其与氧气、pH值和温度等其他变量相关联。仅展示了1988年的数据。春季,锰通过转化为颗粒态从水柱中去除,并沉积到底部沉积物中。这种去除是由于生物因素,因为仅靠湖泊的氧化还原电位/pH值条件无法解释可溶性锰(Mn(II))的氧化。在夏季,微生物还原产生的锰从沉积物转移到水柱中。在分层时期,底部水域中可溶性Mn(II)的浓度会积累到20微摩尔或更高。当发生混合时,可溶性Mn(II)会通过氧化迅速去除。这个循环在夏季会发生不止一次,每个锰原子可能会多次用于有机碳的氧化。在秋季末,整个湖泊的锰浓度稳定下来,并保持在约1微摩尔,直到次年夏季循环再次开始。湖泊的输入和输出表明,活跃的锰循环主要是内部循环,每年会有少量积累到位于湖泊氧化区的铁锰结核中。

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