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1.
The water quality of Dianchi Lake declines quickly and the eutrophication is getting serious. To identify the internal pollution
load of Dianchi Lake it is necessary to evaluate its sediment accumulation. Sedimentation rates of Dianchi Lake are determined
by 137Cs dating. However, 137Cs vertical distribution in sediment cores of Dianchi Lake has special characteristics because Dianchi Lake is located on
the southeast of the Qinghai-Tibet Plateau, the Kunming quasi-stationary front is over the borders of Yunnan and Guizhou where
the specific precipitation is distributed. Besides 1954, 1963 and 1986 137Cs marks can be determined in sediment cores, a 137Cs mark of 1976 representing the major period of 137Cs released from China unclear test can be determined and used for an auxiliary dating mark. Meanwhile Dianchi Lake is divided
into seven sections based on the water depth, basin topography, hydrological features and supplies of silt and the lakebed
area of each section is calculated. The mean annual sedimentation rates for seven sections are 0.0810, 0.1352, 0.1457, 0.1333,
0.0904, 0.1267 and 0.1023 g/cm2a in 1963–2003, respectively. The gross sediment accumulation of the lake is 26.18×104 t/a in recent 17 years and 39.86×104 t/a in recent 50 years.
Foundation: National Natural Science Foundation of China, No.40771186; The Key Project of the State Key Laboratory of Soil Sustainable
Agriculture, Nanjing Institute of Soil Sciences, Chinese Academy of Sciences, No.5022505
Author: Zhang Yan (1962–), Ph.D and Associate Professor, specialized in environmental change. 相似文献
2.
本文对2003年4-12月滇池马村湾、海东湾微囊藻毒素和总磷、总氮、溶解氧、透明度、光照强度、叶绿素a、pH值、水温及微囊藻种群优势度进行了分析,讨论了以上指标在滇池马村湾和海东湾的分布和月变化情况以及与微囊藻毒素含量之间的关系．相关性分析表明马村湾、海东湾微囊藻毒素在水体中分布与总氮和氮磷比之间呈现非常显著的负相关性(P<0．01);与透明度、光照强度和微囊藻种群优势度存在显著的正相关性(P<0．05)．在影响微囊藻毒素的各因素中,运用多因素逐步回归分析得知马村湾、海东湾微囊藻毒素浓度主要南水体的总氮、总磷、叶绿素a和溶解氧以及透明度决定(R2=0．560,P<0．017)． 相似文献
3.
滇池历史地理初步研究 总被引：7，自引：0，他引：7
于希贤 《云南地理环境研究》1999,11(1):7-15
初步研究了地质时代滇池的形成，人类历史时期滇池及周围的环境演变发展的过程，特别是生产活动，文物古迹的分布和气候，动植物的变迁，提出保护自然景观和社会经济发展之间，关系处理好了，是可以和谐共进的。 相似文献
4.
The water quality of Dianchi Lake declines quickly and the eutrophication is getting serious. To identify the internal pollution load of Dianchi Lake it is necessary to evaluate its sediment accumulation. Sedimentation rates of Dianchi Lake are determined by 137Cs dating. However, 137Cs vertical distribution in sediment cores of Dianchi Lake has special characteristics because Dianchi Lake is located on the southeast of the Qinghai-Tibet Plateau, the Kunming quasi-stationary front is over the borders of Yunnan and Guizhou where the specific precipitation is distributed. Besides 1954, 1963 and 1986 137Cs marks can be determined in sediment cores, a 137Cs mark of 1976 representing the major period of 137Cs released from China unclear test can be determined and used for an auxiliary dating mark. Meanwhile Dianchi Lake is divided into seven sections based on the water depth, basin topography, hydrological features and supplies of silt and the lakebed area of each section is calculated. The mean annual sedimentation rates for seven sections are 0.0810, 0.1352, 0.1457, 0.1333, 0.0904, 0.1267 and 0.1023 g/cm2a in 1963–2003, respectively. The gross sediment accumulation of the lake is 26.18×104 t/a in recent 17 years and 39.86×104 t/a in recent 50 years. 相似文献
5.
滇池草海底泥疏挖对水体水质及底泥影响分析研究 总被引：20，自引：1，他引：19
1998年 5月起 ,滇池草海经过近 1年的疏挖 ,清除底泥约 4 0 0× 10 4 m3,使内草海水体质量有明显改善。内湖底质的有机污染物及金属污染物得到有效去除 ,减少了泥层中污染物向水体的扩散 ;大部分水体透明度达到 0 .8m ,已超过沉水植物恢复的需补偿深度 ,为草海水生态恢复创造了条件 ;疏浚区水深增加 ,湖容扩大 ,提高了草海的调蓄能力。但与外草海及外滇池对照点底泥相比 ,草海底泥金属污染物含量仍处较高水平 相似文献
6.
本文研究了蓖齿眼子菜(Potamogeon pectinatus L)在滇池的光合速率、体内叶绿素季节变化及光和水温对其光合速率影响,并根据实验,计算出了蓖齿眼子菜生长的光补偿点,研究结果表明,蓖齿眼子菜1～3月份的净光合产氧量最大,为1.82～1.83mg/(g·h),6月份最低,为0.63 mg/(g·h);植物体内Chl.a和Chl.b平均含量分别为0.25～1.15mg/(g·h)和0.28～0.85mg/(g·h),蓖齿眼子菜可以通过调节体内Chl.a/Chl.b值来适应不同季节生长;蓖齿眼子菜有较宽的水温适应范围,10℃时的净光合产氧量可达0.88mg/(g·h),最高值出现在水温25℃,为1.16mg/(g·h),而30℃以上的水温已表现出对其生长的不利影响;蓖齿跟子菜生长的光补偿点为358～1256Lx,并随温度上升而逐渐增加. 相似文献
7.
8.
The specific methods used for recovery of the aquatic ecological system in the shallow lake are proposed. This research has been done from three aspects:1) the design of the species used for the ecological recovery; 2) the design of optimization and allocation of the aquatic communities; and 3) the design of regional arrangement of the aquatic communities. On the basis of research, the pioneer plant and the species used to establish the communities are proposed. The aquatic plant allocation focuses on the emergent aquatic plant and submergent aquatic plant. Meanwhile, the regional arrangement has been done in the aquatic plant recovery area in the Caohai Lake and the east west bank of the outer lake. 相似文献
9.
借助137Cs估算滇池沉积量 总被引：4，自引：0，他引：4
The water quality of Dianchi Lake declines quickly and the eutrophication is getting serious. To identify the internal pollution load of Dianchi Lake it is necessary to evaluate its sediment accumulation. Sedimentation rates of Dianchi Lake are determined by 137Cs dating. However, 137Cs vertical distribution in sediment cores of Dianchi Lake has special character-istics because Dianchi Lake is located on the southeast of the Qinghai-Tibet Plateau, the Kunming quasi-stationary front is over the borders of Yunnan and Guizhou where the specific precipitation is distributed. Besides 1954, 1963 and 1986 137Cs marks can be determined in sediment cores, a 137Cs mark of 1976 representing the major period of 137Cs released from China unclear test can be determined and used for an auxiliary dating mark. Meanwhile Di-anchi Lake is divided into seven sections based on the water depth, basin topography, hy-drological features and supplies of silt and the lakebed area of each section is calculated. The mean annual sedimentation rates for seven sections are 0.0810, 0.1352, 0.1457, 0.1333, 0.0904, 0.1267 and 0.1023 g/cm2 a in 1963-2003, respectively. The gross sediment accu-mulation of the lake is 26.18×104 t/a in recent 17 years and 39.86×104 t/a in recent 50 years. 相似文献
10.
滇池污染特征及治理对策 总被引：13，自引：0，他引：13
滇池是昆明市的母亲湖，是昆明市的主要水源和经济命脉。近二三十年来，昆明城市规模急剧膨胀，大量污水直接排入滇池，使久负盛名的滇池富营养化。通过深入分析滇池污染的现状和形成原因，提出滇池治理是一项综合性的系统工程，需要寻求新的治理思路和措施，通过改变水流方向和出水口、设立重污染软隔离带、控制农村面源污染、调整产业结构、发展生态农业、恢复流域生态系统等生物、工程措施和经济、政策、法律措施综合协调运用，以实现滇池污染的根本性治理。 相似文献