地球科学进展 ›› 2017, Vol. 32 ›› Issue (6): 651 -659. doi: 10.11867/j.issn.1001-8166.2017.06.0651

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滇池水质特征及变化
张虎才( ), 常凤琴 *( ), 段立曾, 李华勇, 张云鹰, 蒙红卫, 文新宇, 吴汉, 路志明, 毕荣鑫, 张扬, 赵帅营, 康文刚   
  1. 云南师范大学旅游与地理科学学院 高原湖泊生态与全球变化实验室,云南省地理过程与环境变化重点实验室,云南 昆明 650500
  • 收稿日期:2016-12-19 修回日期:2017-04-21 出版日期:2017-06-20
  • 通讯作者: 常凤琴 E-mail:zhanghc@niglas.ac.cn;fqchang@niglas.ac.cn
  • 基金资助:
    云南省领军人才计划“云南高原湖泊演化与水安全研究”(编号:2015HA024);云南省高端人才引进项目“云南(云贵高原)湖泊记录与生态环境及可持续发展研究”(编号:2010CI111)资助

Water Quality Characteristics and Variations of Lake Dian

Hucai Zhang( ), Fengqin Chang( ), Lizeng Duan, Huayong Li, Yunying Zhang, Hongwei Meng, Xinyu Wen, Han Wu, Zhiming Lu, Rongxin Bi, Yang Zhang, Shuaiying Zhao, Wengang Kang   

  1. Key Laboratory of Plateau Lake Ecology & Global Change, Yunnan Provincial Key Laboratory of Geographical Process and Environmental Change on the Plateau, College of Tourism and Geography Science, Yunnan Normal University, Kunming 650500, China
  • Received:2016-12-19 Revised:2017-04-21 Online:2017-06-20 Published:2017-06-10
  • About author:

    First author:Zhang Hucai (1962-), male, Fengxiang County, Shaanxi Province, Professor.Research areas include lake sediment and environmental change.E-mail:zhanghc@niglas.ac.cn

  • Supported by:
    Foundation items:Project supported by the Yunnan Provincial Government Leading Scientist Program “Lake evolution and water security in Yunnan Plateau”(No.2015HA024);Yunnan Provincial Government Senior Talent Program “The lake records and ecological environments in Yunnan and water security”(No.2010CI111)

利用2015年4~9月对滇池从北到南4个部位的水体水温(Temperature或Temp)、溶解氧(DO)、pH值、叶绿素a(Chl-a)、藻蓝蛋白(Phycocyanin或PC) 和电导率(Conductivity或CD)浓度等监测数据,分析了各参数从旱季向雨季转化以及雨季的特征和空间变化;通过表征蓝藻的藻蓝蛋白浓度和所有藻类的叶绿素浓度之比计算获得了水体中的蓝藻相对数量指数(Cyanophyte Relative Quantity Index, CRQI),并估算了蓝藻在湖泊中的相对数量。结果表明:滇池水温经4~5月增温后在6月达到最高值,之后7~9月在保持一定稳定性的背景下逐步降温,水体温度的变化过程不但会受到水深的影响,表现出在快速升温期不同部位升温速度不同、表层水温快的特点。实测数据分析发现,以叶绿素a值所代表的真核生物在4月快速增加并达到最大值,但以藻蓝蛋白所指示的蓝藻却在9月暴发,这与湖泊表层和底层水温一致、溶解氧含量丰富、pH值达最高并均一及水体盐度较低等因素直接相关。

In order to understand the seasonal change tendencies of the water quality of the Lake Dian (Dianchi), the monitoring data from April to September 2015 at four sites distributed in the central part from North to south were analyzed, these data includes the profiles of the water temperature (Temperature or Temp.), Dissolved Oxygen content (DO), pH values, Chlorophyll-a (Chl-a), Phycocyanin (PC) and Conductivity (CD). At the same time, the Cyanophyte Relative Quantity Index (CRQI) was calculated based on the contents of Phycocyanin and Chlorophyll-a. The results demonstrate that along with the air temperature increase, the water temperature also increased step by step from April and May, and reach the maximum in June, from July to September, the water temperature kept relatively stable and decrease steadily. It also shows that the water temperature is not only various with different water depth, but also show that the temperature increase at different speed, even generally show that the surface temperature increase more rapidly than the deep water. The water temperature and its changes may adjust the air temperature of Kunming strongly and therefore, it is important for the forming of the Four Springs City of Kunming. We found that the amount of eukaryotes represented by Chlorophyll-a increased quickly and reach the highest level in the April, but the blue-green algae, which represented by the Phycocyanin is blooming in the September. This might imply that when the blue-green algae dominated the algae, the algae blooming occur. This is of great importance to understand the algae blooming processes in Lake Dian. We hope the further monitoring will provide us more detailed and useful information. Mean while, the changes of DO, pH and CD all have shown their unique that inspire us to continue the lake water monitoring. This monitoring work also proves that the single site measurements cannot provide any reliable and useful information about the lake water quality. More detailed and sustained monitoring works need to be done before we have a fully understanding on the changes of the lake water quality.

中图分类号: 

图1 滇池及其流域和监测点分布图
Fig.1 Lake Dian and its drainage area, monitoring sites
图2 滇池水温垂直剖面图
Fig.2 Vertical profile of water temperature in Lake Dian
图3 滇池溶解氧垂直剖面图
Fig.3 Vertical profile of Dissolved Oxygen (DO) in Lake Dian
图4 滇池pH垂直剖面图
Fig.4 Vertical profile of pH in Lake Dian
图5 滇池电导率垂直剖面图
Fig.5 Vertical profile of conductivity in Lake Dian
图6 滇池叶绿素a垂直剖面图
Fig.6 Vertical profile of chlorophyll in Lake Dian
图7 滇池藻蓝蛋白垂直剖面图
Fig.7 Vertical profile of Phycocyanin (PC) in Lake Dian
图8 滇池蓝藻相对数量指数^图中纵坐标数值由公式CRQI=[PC]/[chl-a]计算而来,其单位为cells/mg
Fig.8 Cyanophyte Relative Quantity Index in Lake Dian^The index CRQI, with the unit of cells/mg, was calculated using equation of CRQI=[PC]/[chl-a], where PC=phycocyanin
[1] Wang Hongmei, Chen Yan.Change trend of eutrophication of Dianchi Lake and reason analysis in recent 20 years[J]. Environmental Science Survey, 2009, 28(3): 57-60.
[王红梅, 陈燕. 滇池近20a富营养化变化趋势及原因分析[J]. 环境科学导刊, 2009, 28(3): 57-60.]
[2] Zhang Hucai.The potential endangers of the tectonic lake water leakage from Dianchi and water security[J]. Advances in Earth Science, 2016, 31(8):849-857, doi:10.11867/j. issn. 1001-8166. 2016. 08. 0849.
[张虎才. 滇池构造漏水隐患及水安全[J]. 地球科学进展, 2016, 31(8): 849-857, doi:10.11867/j.issn. 1001-8166. 2016.08.0849.]
[3] Zhang Hucai.Can water hyacinth clean highly polluted waters?[J].Journal of Environmental Protection, 2012,(3):340-341.
[4] Li Zhongjie, Zheng Yixin, Zhang Dawei, et al.Impacts of 20-year socio-economic development on aquatic environment of Lake Dianchi Basin[J]. Journal of Lake Sciences, 2012, 24(6): 875-882.
[李中杰, 郑一新, 张大为, 等. 滇池流域近20年社会经济发展对水环境的影响[J]. 湖泊科学, 2012, 24(6):875-882.]
[5] He Jia, Xu Xiaomei, Yang Yan, et al.Problems and affects of comprehensive management of water environment in Lake Dianchi[J]. Journal of Lake Sciences, 2015, 27(2):195-199.
[何佳, 徐晓梅, 杨艳, 等. 周鸿斌.滇池水环境综合治理成效与存在问题[J]. 湖泊科学, 2015, 27(2):195-199.]
[6] Jacob Kalff,ed. Gu Binhe, Liu Zhengwen, Li Kuanyi, et al, translated. Franslated Limnology—Inland Water Ecosystems[M]. Beijing: Higher Education Press, 2011.
[Jacob Kalff,著. 古滨河, 刘正文, 李宽意, 等,译. 湖沼学——内陆水生态系统[M]. 北京: 高等教育出版社, 2011.]
[7] Pang Xiaoyu, Duan Hongtao, Zhang Yuchao, et al.Comparison of the extraction methods of phycocyanin pigments in eutrophic lake waters[J]. Journal of Lake Sciences, 2014, 26(5): 799-806.
[庞晓宇, 段洪涛, 张玉超, 等. 富营养化湖泊水体中藻蓝蛋白提取方法的对比[J]. 湖泊科学, 2014, 26(5):799-806.]
[8] Yin Bin.Blue Algae Estimation Based on MERIS Data in Taihu Lake[D]. Nanjing:Nanjing Normal University, 2011.
[尹斌. 基于MERIS数据的太湖蓝藻估算研究[D].南京:南京师范大学, 2011.]
[9] Wang Bin, Ma Jian, Wang Yinya, et al.Seasonal characteristics of thermal stratification in Lake Tianchi of Tianshan Mountains[J]. Journal of Lake Sciences, 2015, 27(6): 1 197-1 204.
[王斌, 马健, 王银亚, 等. 天山天池水体季节性分层特征[J]. 湖泊科学, 2015, 27(6): 1 197-1 204.]
[10] Huang Lei, Wang Junbo, Zhu Liping,et al.Water temperature and characteristics of thermal stratification in Nam Co, Tibet[J]. Journal of Lake Sciences, 2015, 27(4):711-718.
[黄磊, 王君波, 朱立平, 等. 纳木错水温变化及热力学分层特征初步研究[J]. 湖泊科学, 2015, 27(4):711-718.]
[1] 张虎才. 滇池构造漏水隐患及水安全[J]. 地球科学进展, 2016, 31(8): 849-857.
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