1. 宁夏大学 土木与水利工程学院,宁夏,银川,750021
2. 宁夏大学 生命科学学院,宁夏,银川,750021
纸质出版:2019
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李延林, 邱小琮. 沙湖的水环境容量和污染物总量控制[J]. 水土保持通报, 2019,39(5):272-277.
Li Yanlin, QIU Xiaocong. Environmental Capacity and Total Pollutant Control in Shahu Lake[J]. Bulletin of Soiland Water Conservation, 2019, 39(5): 272-277.
李延林, 邱小琮. 沙湖的水环境容量和污染物总量控制[J]. 水土保持通报, 2019,39(5):272-277. DOI: 10.13961/j.cnki.stbctb.2019.05.038.
Li Yanlin, QIU Xiaocong. Environmental Capacity and Total Pollutant Control in Shahu Lake[J]. Bulletin of Soiland Water Conservation, 2019, 39(5): 272-277. DOI: 10.13961/j.cnki.stbctb.2019.05.038.
[目的] 探明宁夏回族自治区沙湖富营养化状态及计算主要污染的水环境容量,为沙湖入湖污染负荷的削减和水环境保护提供一定依据。[方法] 于2015-2017年冬(1月)、春(4月)、夏(7月)、秋(10月)监测了沙湖水体理化指标。采用综合营养状态指数法对其富营养化状态进行了评价,采用沃伦威德(Vollenweider)模型和狄龙(Dillion)模型计算了4种不同水质目标情景下的高锰酸盐指数、总氮和总磷的水环境容量。[结果] 2015-2017年沙湖富营养化状态总体上为春、冬季轻度富营养化,夏、秋季中度富营养化;情景二和三水质目标下沙湖2015-2017年高锰酸盐指数,总氮和总磷水环境容量剩余量均为0;情景四水质目标下沙湖2015-2017年总磷的水环境容量剩余量均为0,高锰酸盐指数的水环境容量有剩余量,总氮的水环境容量2015年有剩余量,2016-2017年剩余量为0。在2017年水质现状的基础上,达到Ⅲ类水质要求高锰酸盐指数、总氮和总磷分别消减655.97 t,39.27 t和1.41 t,消减率分别为112.89%,45.58%和37.60%;达到Ⅳ类水质要求高锰酸盐指数、总氮和总磷分别消减0,15.83 t和0.94 t,消减率分别为0,18.37%和25.07%。[结论] 沙湖水体呈现一定程度的污染,已达到富营养化状态,高锰酸盐指数、总氮和总磷的水环境容量大于目标要求的水环境容量,应该及时进行治理和保护。
[Objective] This study aims to determine the eutrophication status of Shahu Lake
Ningxia Hui Autonomous Region
and to calculate the environmental capacity of the lake for major pollution as a means of providing a basis for reducing the pollution load and improving the environmental protection of Shahu Lake.[Methods] Water samples were collected in January
April
July
and October during 2015-2017 to measure physical and chemical parameters. A comprehensive eutrophic state index was applied to assess the trophic status
and the Vollenweider and Dillon model was used to analyze the environmental capacity of permanganate index(CODMn)
total nitrogen (TN)
and total phosphorus (TP) of the lake under four different water quality target scenarios.[Results] During 2015-2017
Shahu Lake was mildly eutrophic in spring and winter
and moderately eutrophic in summer and autumn. In scenarios two and three of the water quality targets
the remaining environmental capacities for CODMn
TN and TP were zero. In scenario four
the remaining environmental capacity of the lake for TN was zero
whereas that for CODMn still had a remaining capacity. The environmental capacity of TN had a surplus in 2015
but this was reduced to zero in 2016-2017. On the basis of the water quality in 2017
to attain class Ⅲ water quality requirements
CODMn
TN
and TP should be reduced to 655.97
39.27
and 1.41 tonnes
respectively
which correspond to reduction rates of 112.89%
45.58%
and 37.60%
respectively. In order to attain class Ⅳ water quality requirements
the CODMn
TN and TP should be reduced by 0.0
15.83
and 0.94 tonnes
respectively
which correspond to reduction rates of 0%
18.37%
and 25.07%
respectively.[Conclusion] Shahu Lake has certain degree of pollution and has reached a state of eutrophication
the environmental capacities of CODMn
TN
and TP in the lake are greater than the target requirement
and should be managed and protected.
Phillips G, Kelly A, Pitt J, et al. The recovery of a very shallow eutrophic lake, 20 years after the control of effluent derived phosphorus[J]. Freshwater Biology, 2010,50(10):1628-1638.
Guo L. Ecology:Doing battle with the green monster of Taihu Lake[J]. Science, 2007,317(5842):1166-1166.
Xu Fuliu, Tao Shu, Dawson R W, et al. Lake ecosystem health assessment:indicators and methods[J]. Water Research, 2001,35(13):3157-3167.
Yu Tao, Zhang Yuan, Wu Fengchang, et al. Six-decade change in water chemistry of large freshwater lake Taihu, China[J]. Environmental Science & Technology, 2013,47(16):9093-9101.
何德进,邢友华,姜瑞雪,等.东平湖水体中氮磷的分布特征及其富营养化评价[J].环境科学与技术, 2010,33(8):45-48,61.
Baulch H M. Asking the right questions about nutrient control in aquatic ecosystems[J]. Environmental Science & Technology, 2013,47(3):1188-1189.
张晟,李崇明,郑坚,等.三峡水库支流回水区营养状态季节变化[J].环境科学,2009,30(1):64-69.
金相灿.湖泊富营养化控制和管理技术[M].北京:化学工业出版社,2001.
王霞,吕宪国,闫伯茹,等.基于富营养化阈值的松花湖水环境容量分析[J].湖泊科学, 2006,18(5):503-508.
郝芳华.流域水质模型与模拟[M].北京:北京师范大学出版社,2008.
罗燕珠,璩向宁.宁夏沙湖历年水质变化趋势分析[J].水土保持通报,2011,31(5):246-249.
鲁小珍,刘茂松,胡海波,等.宁夏沙湖风景区的生态环境问题与对策[J].南京林业大学学报:自然科学版,2001,25(3):89-92.
任学蓉,郎勇设,金辉.沙湖水体富营养化评价及防治对策[J].干旱区资源与环境,2007,21(2):118-122.
赵红雪,邱小琮,杨艳梅,等.宁夏沙湖水体富营养化分析与评价[J].湖北农业科学,2010,49(10):2414-2417.
陈珂,张健,李娇,等.宁夏平罗沙湖水体富营养化变化特征分析及防治对策[J].宁夏农林科技,2016,57(11):56-58,63.
张小东.福建省棉花滩水库富营养化状况评价及分析[J].水生态学杂志,2012,33(5):20-24.
王明翠,刘雪芹,张建辉.湖泊富营养化评价方法及分级标准[J].中国环境监测,2002,18(5):47-49.
金相灿.中国湖泊环境[M].北京:海洋出版社,1995.
中国标准化管理委员会,中华人民共和国国家质量监督检验检疫总局. GB/T25173-2010水域纳污能力计算规程[S].北京:中国标准出版社,2010.
逄勇,陆桂华.水环境容量计算理论及应用[M].北京:科学出版社,2010.
国家环境保护总局,中华人民共和国国家质量监督检验检疫总局. GB 3838-2002地表水环境质量标准[S].北京:中国标准出版社,2002.
于凤存,方国华,徐佳,等.中小型湖库型饮用水水源地污染负荷总量控制探讨[J].水文,2015,35(4):42-46,19.
Martin J R, Keller C H, Jr C R, et al. Long-term performance summary for the Boot Wetland treatment system[J]. Water Science & Technology, 2001,44(11/12):413-420.
刘信安,湛敏,马艳娥.三峡库区流域藻类生长与营养盐吸收关系[J].环境科学,2005,26(4):95-99.
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