三峡库区典型农业小流域溶解性有机质(DOM)的地球化学特征分析
[Abstract]:As the sensitive ecological environment system of the Three Gorges Reservoir, its unique "dry and wet alternation" characteristics have been widely concerned since the water storage. It is an active area of the physical and energy transfer and transformation of the water and surrounding land ecosystem in the reservoir area, and has the function of buffer zone and plant bank protection, and is quite sensitive to the response of the external change. The agricultural small watershed system, which is based on the slope land, plays an important role in the ecological environment quality of the reservoir in the reservoir area. As an important part of the global carbon cycle, DOM has an important influence on the global climate change, and it is also an important active component of the material and energy circulation in the ecosystem, which is closely related to many important links in the ecosystem. Because of the active role of the DOM, the important influence of the DOM on the water environment in the agricultural small watershed will undoubtedly further affect the environmental behavior of the nutrient elements, heavy metals, organic pollutants and greenhouse gases in the region. On the basis of this, the study has selected the small watershed of Wangjiagou, the typical agricultural small watershed in the Three Gorges Reservoir area, which is the object of the small watershed. in ord to clarify that heterogeneity of the DOM geochemical characteristics in the soil and the water body of the typical agricultural small watershed, The results show that: (1) The difference of DOM in different land-use conditions is obvious, and the soil DOM of the forest land has a high degree of aromaticity, and the humification is the strongest, and the second is the field; Although the content of soluble organic carbon (DOC) was high (80.69 mg 路 L-1 and 89.20 mg 路 L-1, respectively), the degree of aromatalization was low and the contribution of the non-chromophoric component in the DOM to the high DOC content was significant. The fluorescence index (FI) of all samples is between the self-source characteristics (FI = 1.9) and the land-source characteristics (FI = 1.4), and the self-generated (class-like component) and the isogenic (species-like humic components) contribute to the DOM. Most of the soil sample class protein/ humic fluorescent component (r (T/ C)) is greater than 2.0, indicating that the soil DOM of the agricultural small watershed is influenced by external factors, especially human activities, especially in the vegetable field. in addition, that sensitivity of the different UV-and fluorescence spectral parameters to the difference of the DOM structure and the property in different land-use conditions is different, and the ratio of the spectral slope (SR) and the humification index (HIX) cannot reflect the difference of the characteristic of the DOM, Therefore, the single ultraviolet-visible or fluorescent spectrum index can not provide the characteristic information of the DOM in a comprehensive way, and it is suggested that the two spectral analysis methods can be used in combination. (2) The soluble organic matter (DOM) plays an important role in the water environment of the basin as an important geochemical factor. There is a large difference in the dom space between the water bodies in the small watershed, and the composition and the source of the water are obviously different. The order of the size of the colored soluble organic matter (cdrom) in the dom (ag * (355)) is: the water outlet of the water in the water and the water in the paddy field of the rice field, wherein the suva254 of the rice field water and the ditch water is larger than the well water and the outlet water, and the aromatic property is more obvious. There are four fluorescence peaks (a, c and b, t) in the three-dimensional fluorescence spectrum, both of which are the dual contribution of the inside (micro-organisms, algae) and the foreign (humus). In addition to the influence of the microbial activity of the biogenic source, the influence of the exogenous domestic sewage and the water for agricultural production is also an important cause of the increase of the protein-like components in the dom component. The dom spectral characteristics of the water samples at the same location in different planting season are compared, and the component of the class protein is an important factor to control the fluctuation of the dom characteristics of the two planting seasons. There was a significant difference in r (t/ c) among the water body doc, cdrom and dom after the change of the land use method, and the difference of fi, the self-source index (bix) and the humification fluorescent component (r (a/ c)) at the short-wave and long-wave sites was not significant. (3) The different types of soil doc storage capacity of different land use types show different characteristics. The maximum capacity of doc is 0.798 mg 路 g-1, the structure is more complex, the lowest of the field is 0.237 mg 路 g-1.dom, the non-chromophoric component has an important contribution to the high doc content. There was no significant correlation between ccom and doc in different extraction ratios (p0.05). The results of principal component analysis show that the change of the capacity of doc library is influenced by the self-source microbial activity and the external human factors. Due to the comprehensive influence of external photodegradation and human factors, the correlation between the capacity of the four types of soil doc and the parameters of dom's spectral parameters is different, and the single spectral index can not accurately reflect the change of the capacity of the doc library, and it is suggested that the combination of the two indexes of the ultraviolet and the fluorescence spectrum can be combined. The adsorption equilibrium constant ks has a very significant positive correlation with the dissolved organic carbon library capacity[doc], and the soil with large adsorption constant has higher doc storage capacity. (4) The fluorescence organic matter (fdom) and cdrom of the water sample dom in the whole year of the small watershed were significantly correlated with the doc (p0.05). The order of the concentration of the different sampling time doc was: April, November, November. The variation range of the concentration of doc (a (355)] in the range of from 1.22 to 165.00 mg 路 l-1 and the concentration of fdom[a (355)] varied from 0.08 to 24.47 m-1, and the range of fdom concentration[fn (355)] ranged from 2063.80 to 102811.99 m-1. The order of the fluorescence intensity of a different sample time class of protein material (peakb and peakt) was April, November, November. The variation range of fi-value is 1.55-1.75, between the land-source characteristic value 1.40 and the intrinsic contribution value of 1.90, and dom is influenced by the endogenous contribution and the exogenous input. There was a significant difference in the self-source contribution, the aromaticity, the hydrophobic component size and the molecular weight of the sub-1 and sub-2 of the two small watersheds. In summer, the degree of water dom in the small watershed is the highest, the self-source is more obvious, the component of the class protein is relatively large, and the bioavailability is high; in the spring, the water sample of autumn is in the middle of the humification degree, and the winter is the weakest. There was a significant positive correlation between the water content (thg) and the sr (p0.05), and the significant negative correlation with fi (p0.05), and a significant negative correlation with fi (p0.05), while there was a significant negative correlation with fi (p0.05). (5) Dissolved organic matter (Dom) is an important part of the water body ecosystem, and its nature and structure decide that it plays an important role in the environmental behavior of the pollutants (for example, the effect on the migration and transformation of the mercury). In addition, there is no significant correlation between SUVA 254 and DOC, but the color and molecular weight of the water body are important factors for controlling the dissolved state and active mercury; the change of methylmercury may be closely related to the enrichment and migration of organic matter caused by primary productivity of the water body.
【学位授予单位】:西南大学
【学位级别】:硕士
【学位授予年份】:2016
【分类号】:X52
【相似文献】
相关期刊论文 前10条
1 许中坚,刘广深,刘维屏;土壤中溶解性有机质的环境特性与行为[J];环境化学;2003年05期
2 郭杏妹;吴宏海;王伟伟;曾丁才;林怡英;;土壤溶解性有机质及其表面反应性的研究进展[J];生态科学;2007年01期
3 唐东民;伍钧;陈华林;周江敏;祝亮;;溶解性有机质对苄嘧磺隆在土壤中吸附解吸行为的影响[J];农业环境科学学报;2008年05期
4 徐慧;;溶解性有机质对土壤中污染物环境行为的影响[J];安徽农业科学;2009年03期
5 王志霞;葛小鹏;晏晓敏;林进;周岩梅;王东升;;溶解性有机质对菲在沉积物上吸附与解吸性能的影响[J];中国环境科学;2012年01期
6 沈亚婷;;土壤溶解性有机质对植物吸收-输送-贮存重金属的影响研究现状与进展[J];岩矿测试;2012年04期
7 郑晓冬;乔显亮;肖杰;王晓晨;;水中溶解性有机质对三氯生光解的影响[J];环境科学与技术;2013年10期
8 吴济舟;张稚妍;孙红文;;无机离子对芘与天然溶解性有机质结合系数的影响[J];环境化学;2010年06期
9 杨帆;朱晓敏;黄清辉;李建华;;崇明岛前卫湖水中有色溶解性有机质的分布和来源[J];生态与农村环境学报;2008年03期
10 陈同斌,陈志军;土壤中溶解性有机质及其对污染物吸附和解吸行为的影响[J];植物营养与肥料学报;1998年03期
相关会议论文 前6条
1 陈华林;周江敏;Weilin Huang;潘叶敏;钟春节;;溶解性有机质分组组分对土壤吸附芘的影响[A];中国矿物岩石地球化学学会第12届学术年会论文集[C];2009年
2 王廷廷;余向阳;刘贤金;张超兰;;土壤可溶性有机质对生物质炭吸附氯虫苯甲酰胺的影响[A];第六届全国环境化学大会暨环境科学仪器与分析仪器展览会摘要集[C];2011年
3 肖小雨;邱宇平;盛光遥;;溶解性有机质对黑碳吸附敌稗的抑制作用[A];第五届全国环境化学大会摘要集[C];2009年
4 Sheela G.Agrawal;Ryan L.Fimmen;Yuping Chin;马丽颖;;黄腐酸和湖泊微孔水对Fe(Ⅱ)还原Cr(Ⅵ)为Cr(Ⅲ)的影响[A];第八届全国绿色环保肥料(农药)新技术、新产品交流会论文集[C];2009年
5 吴文伶;孙红文;汪磊;;人工及天然表面活性剂对菲的分配[A];持久性有机污染物论坛2008暨第三届持久性有机污染物全国学术研讨会论文集[C];2008年
6 张闻;卢媛;张艳伟;孙红文;;土壤溶解性有机质对黑炭吸附芘的影响[A];中国化学会第27届学术年会第02分会场摘要集[C];2010年
相关博士学位论文 前1条
1 凌婉婷;溶解性有机质对莠去津在土壤/矿物-水界面行为的影响及其机理研究[D];浙江大学;2005年
相关硕士学位论文 前10条
1 王艳姣;全氟化合物与溶解性有机质在PM_(2.5)中的污染特征[D];复旦大学;2014年
2 李任政;煤矿区地下水中溶解性有机质的迁移转化规律研究[D];河南理工大学;2015年
3 王齐磊;三峡库区典型农业小流域溶解性有机质(DOM)的地球化学特征分析[D];西南大学;2016年
4 杨兰兰;溶解性有机质DOM对典型抗生素甲硝唑光降解的影响研究[D];东华大学;2016年
5 赵劲松;污染对土壤溶解性有机质及特征化合物影响的研究[D];东北师范大学;2002年
6 祝亮;溶解性有机质的动态变化及对铜锌吸附—解吸行为的影响[D];四川农业大学;2008年
7 唐东民;溶解性有机质的动态变化及其对有机物吸附解吸的影响[D];四川农业大学;2008年
8 肖q辖,
本文编号:2480359
本文链接:https://www.wllwen.com/shengtaihuanjingbaohulunwen/2480359.html