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洱海沉积物水提取态有机氮特征及与其他来源溶解性有机氮的差异
引用本文:李文章,张莉,王圣瑞,肖尚斌,钱伟斌,席银,许可宸,史玲珑.洱海沉积物水提取态有机氮特征及与其他来源溶解性有机氮的差异[J].环境科学,2017,38(7):2801-2809.
作者姓名:李文章  张莉  王圣瑞  肖尚斌  钱伟斌  席银  许可宸  史玲珑
作者单位:三峡大学水利与环境学院, 宜昌 443002;中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,三峡大学水利与环境学院, 宜昌 443002;中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,三峡大学水利与环境学院, 宜昌 443002,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,三峡大学水利与环境学院, 宜昌 443002;中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护湖泊污染控制重点实验室, 北京 100012;云南省高原湖泊流域污染过程与管理重点实验室, 昆明 650504
基金项目:国家自然科学基金项目(U1202235,41503113);国家水体污染控制与治理科技重大专项(2012ZX07105-004);环境基准与风险评估国家重点实验室自由探索项目(2014-GOT-042-N-06)
摘    要:选取洱海不同季节全湖47个沉积物表层样品,探讨水提取态有机氮(WEON)与不同来源(上覆水、间隙水、入湖河流和湿沉降)溶解性有机氮(DON)组分特征差异,并分析其对沉积物影响.结果表明,(1)洱海沉积物WEON含量季节性变化为夏季春季秋季冬季;空间分布规律呈北部南部中部.(2)洱海沉积物WEON腐殖化程度较高,腐殖质主要以富里酸为主,主要含有紫外区类腐殖质荧光峰A和高激发类色氨酸荧光峰B,受陆源输入和湖内生物共同影响.(3)洱海沉积物及其他来源DON均含有2个荧光组分,其中组分C1为内源性可见紫外区腐殖质峰是生物降解形成的荧光峰;组分C2为类色氨酸峰;湿沉降样品类蛋白峰峰强最大,生物可利用性较高;入湖河流DON生物可利用性最低.(4)洱海上覆水DON荧光C1和C2组分和沉积物WEON含量为显著相关(r=-0.79,P0.01;r=-0.944,P0.01),上覆水DON的荧光组分特征能够很好指示沉积物WEON含量特征.研究洱海不同样品DON结构组分特征,揭示洱海富营养化的潜在风险,为防治规划提供依据.

关 键 词:溶解性有机氮  沉积物  水提取态有机氮  三维荧光光谱  平行因子分析法
收稿时间:2016/12/7 0:00:00
修稿时间:2017/2/24 0:00:00

Characteristics of Water Extractable Organic Nitrogen from Erhai Lake Sediment and Its Differences with Other Sources
LI Wen-zhang,ZHANG Li,WANG Sheng-rui,XIAO Shang-bin,QIAN Wei-bin,XI Yin,XU Ke-chen and SHI Ling-long.Characteristics of Water Extractable Organic Nitrogen from Erhai Lake Sediment and Its Differences with Other Sources[J].Chinese Journal of Environmental Science,2017,38(7):2801-2809.
Authors:LI Wen-zhang  ZHANG Li  WANG Sheng-rui  XIAO Shang-bin  QIAN Wei-bin  XI Yin  XU Ke-chen and SHI Ling-long
Affiliation:College of Hydraulic & Environmental Engineering, China Three Gorges University, Yichang 443002, China;State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China,College of Hydraulic & Environmental Engineering, China Three Gorges University, Yichang 443002, China;State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China,College of Hydraulic & Environmental Engineering, China Three Gorges University, Yichang 443002, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China,College of Hydraulic & Environmental Engineering, China Three Gorges University, Yichang 443002, China;State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China and State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory for Lake Pollution Control, Research Center of Lake Eco-environment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;Yunnan Key Laboratory of Pollution Process and Management of Plateau Lake-Watershed, Kunming 650504, China
Abstract:The 47 samples from Erhai Lake surface sediments were collected in different seasons. The distribution and structure characteristics of sediment water extractable organic nitrogen(WEON) were investigated by using the combined techniques of UV-Vis absorption and three-dimensional excitation-emission matrix spectra(3DEEMs). The differences in DON of various sources(overlying water, pore water, inflow Rivers and wet deposition) were explored to analyze its effects on sediment. The results showed that:1the temporal distribution followed the pattern of summer > spring > autumn > winter, with the spatial WEON distribution of northern > southern > central. 2 The humic degree of Erhai sediment WEON was relatively high and mostly composed of fulvic acid, which mainly contained UV-like humic-like fluorescence peak A and high-excited tryptophan fluorescence peak B. This indicated that it was mainly affected by terrestrial input and microbial activity. 3 There were two fluorescent components(C1, C2) in the sediments and other sources of Erhai Lake. The component C1 was the endogenous visible ultraviolet peak formed by biodegradation, while the component C2 was the tryptophan peak. The bioavailability of wet deposition samples was comparatively high, greatly impacting Erhai Lake in heavy rainfall. The DON bioavailability in the inflow river was the lowest, which was prone to be accumulated in sediments. 4The DON component C1 and C2 in overlying water had significant negative correlation with Erhai sediment WEON contents(r=-0.79, P<0.01;r=-0.944, P<0.01). This suggested that the overlying water DON components could indirectly reflect the sediment WEON content of Erhai Lake, namely the higher the fluorescence components C1 and C2 in overlying water DON were, the lower the sediment WEON content was.
Keywords:dissolved organic nitrogen(DON)  sediment  water extractable organic nitrogen(WEON)  EEMs  EEM-PARAFAC
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