两淮采煤沉陷区水域水体富营养化及氮、磷限制模拟实验

选取两淮采煤沉陷区内3个不同营养水平的水域为研究站点,即淮北南湖站(HBNH)、淮南潘谢顾桥站(PXGQ)和潘谢谢桥站(PXXQ),首先分析了水体营养盐含量、比例结构和营养状态指数,3个站点TP浓度的年均值分别为0.056、0.064和0.092 mg/L,TN浓度年均值则为1.00、0.94和2.67 mg/L,3个站点水体呈现"中营养-轻度富营养"和"中度富营养"2种营养状态,总体上表现出P相对N缺乏的特征.设置对照组、加氮组、加磷组和加氮磷组开展秋季氮、磷限制模拟实验研究.结果表明:HBNH、PXXQ两个站点为P限制,而PXGQ站点则为N限制.尽管水体正磷酸盐浓度较低,但由于藻类具有利用有机磷或储备P库的能力,3个研究站点依然保持了较高的初级生产力,HBNH、PXGQ和PXXQ 3个站点的叶绿素a浓度年均值分别为13.07、26.95和46.25 mg/m³,与各水体的营养水平保持一致.两淮采煤沉陷区水体富营养化控制关键可能在于调控磷元素的水平.     

Influence of land use on the persistence effect of riverine phosphorus

The persistence effect contribution of legacy nutrients is often cited as a reason for little or no improvement in water quality following extensive implementation of watershed nutrient mitigation actions, yet there is limited knowledge concerning factors influencing this response, often called the “persistence effect.” Here, we adopted detrended fluctuation analysis and Spearman analysis methods to assess the influence of land use on the watershed phosphorus (P) persistence effect, using monthly water quality records during 2010–2016 in 13 catchments within a drinking water reservoir watershed in eastern China. Detrended fluctuation analysis was used to calculate the Hurst exponent α to assess watershed legacy P characteristics (α  ≈ 0.5, α  > 0.5, and α  < 0.5 indicate white noise, persistence, and anti‐persistence, respectively). Results showed weak to strong P persistence (0.60–0.81) in the time series of riverine P in the 13 catchments. The Hurst exponent α had negative relationships with agricultural land (R = ?.47, p = .11) and developed land (R = ?.67, p = .01) and a positive relationship with forest land cover (R = .48, p = .10). The persistence effect of riverine P was mainly determined by retention ability (biogeochemical legacy) and migration efficiency (hydrological legacy). A catchment with strong retention capacity (e.g., biomass uptake/storage and soil PO₄ sorption) and low migration efficiency results in a stronger persistence effect for riverine P. In practice, source control is more effective in catchments with weak persistence, whereas sink control (e.g., riparian buffers and wetlands) is preferred in catchments with strong persistence effects.     

典型富营养化城市河流——浙江温瑞塘河的浮游植物群落类型与季节变化

为评估温瑞塘河水环境状况及水华风险,于2015年每月15日7:00-18:00对其下游滞流河段进行高频监测分析,考察了水体叶绿素a浓度、浮游植物群落类型和光合活性等的季节变化及日变化情况,并分析了其与温度、营养盐等环境因子的关系.结果表明:温瑞塘河表层水体中的叶绿素a浓度表现为春季(3-5月)夏季(6-8月)秋季(9-11月)冬季(12-2月),分别为39.98、37.62、21.59和10.74μg/L;4个季节的平均水温则是夏季秋季春季冬季,分别为30.91、25.34、20.72和13.80℃.全年总氮浓度为5.33±0.81~9.40±1.25 mg/L,总磷浓度为0.32±0.18~0.95±0.25mg/L,营养程度属于超富营养.温瑞塘河的浮游植物群落类型为硅藻-绿藻型,全年以绿藻和硅藻种群为主,蓝藻种群只在春末夏初出现,并且所占比例很小.绿藻种群在夏季占绝对优势,而硅藻种群在冬季占优势.绿藻种群的相对丰度与水温呈正相关,而硅藻种群的相对丰度与水温呈负相关.水体的叶绿素a浓度与水温呈正相关,而与总氮、总磷浓度没有相关性.叶绿素a在不同季节呈现出不同的日变化模式,而浮游植物的有效光合量子产率在四季均呈现类似的日变化模式:都是先降后升,与晴天时的日照强度变化趋势相反.绿藻的有效光合量子产率高于硅藻,且除春季外皆存在显著差异.以上结果表明温瑞塘河具备发生各类水华的营养条件,但是由于蓝藻在全年所占的比例都很低,因此发生蓝藻水华的可能性很小;同时由于日照变化会对表层水体中叶绿素a浓度及浮游植物生理活动产生影响,因此在对小型湖泊或者水流滞缓的河道进行浮游植物群落结构调查时还应考虑时间和天气因素.     

不同供氧方式对水库底泥氮磷释放的影响

采用实验室模拟试验,研究了三种供氧方式——曝气、投加过氧化氢和投加过氧化钙对水库底泥氮磷释放的影响.研究结果表明:(1)溶解氧是控制底泥氮磷释放的重要因素,厌氧条件能加速底泥释放磷和氨氮;(2)曝气、投加过氧化氢和投加过氧化钙均能显著提高底部水体的溶氧水平,并能有效抑制底泥氮磷的释放.三种供氧方式对底泥释磷的控制效率依次为:投加CaO2>曝气>投加H2O2;对氨氮释放的控制效率则为:曝气>投加CaO2>投加H2O2.     

Study of chemical forms of phosphorus and their bioavailability in the sediments

Chemical forms of phosphorus in the sediments of the Daya Bay, the Zhujiang River estuary, and the Xiamen Bay are measured with extraction solutions of MgCl2, NaOH, and HCl. Their availabilities to Chlorella sp. and Isochrysis galbana are estimated by using sediments as the sole source of P in the bioassays. The results show that the contents of total phosphorus (TP) in these sediments are 449.3, 650.1 and 643.9 mg/kg, respectively. The contents of non-apatite inorganic P (NAIP) extracted with MgCl2 and NaOH from 3 sediments are 168.8, 146.6 and 118.1 mg/kg,respectively, and account for 18.3%～32.6% of TP. The phosphorus extracted with HCI solution is greater than that extracted with NaOH solution and the lowest extracted P is MgCl2-extractable P. The greatest relative growth rates of Chlorella sp. and Isochrysis galbana cultured with sediments are in the range of 4.3%～26.9%. The increasing biomasses of these algae correspond to NAIP and AAPP (the estimated algal-available particulate P). AAPP accounts for 42.4%～78.2% of NAIP, 21.1%～27.1% of total inorganic P, and 11.8%～20.3% of TP, respectively.     

基于污染负荷核算的岷江流域总磷污染成因分析及对策

总磷是长江流域水环境污染的首要超标因子,岷江作为长江上游流量最大的支流,总磷污染严重,对长江总磷污染贡献较大。为了解岷江流域总磷污染,采用排污系数法,计算得到2016年岷江流域污染源总磷入河量为1 154 t,以农村生活污染负荷占比最高(51.3%),其次为城镇生活源(28.7%)、农业非点源(8.24%)、工业源(9.57%)、畜禽养殖源(1.21%),城市径流源(0.99%)最低;在空间上岷江流域总磷污染负荷呈中游(64.2%)>下游(32.6%)>上游(3.1%)的特点,与岷江干流总磷浓度变化趋势相符,其中成都市总磷污染负荷最高(51.2%),与区域人口密度高、生产和生活活动密集有关。结合资料收集和现场调查,岷江流域总磷污染成因主要包括农村生活污染治理缺口较大、城镇生活污染处理基础设施建设不足、工业企业密布、部分支流总磷污染严重、水污染治理导向不全面。针对岷江总磷污染负荷分布特征及成因,提出“上游保护优质水体、中游治理重污染水体、下游恢复不达标水体”的分区污染防治对策,统筹流域监管体制机制,强化岷江流域水环境保护和治理。     

The composition of nutrient fluxes from contrasting UK river basins

Accurate estimates of N and P loads were obtained for four contrasting UK river basins over a complete annual cycle. The fractionation of these loads into dissolved and particulate, and inorganic and organic components allowed a detailed examination of the nutrient load composition and of the factors influencing both the relative and absolute magnitude of these components. The particulate phosphorus (TPP) loads account for 26–75% of the annual total phosphorus (TP) transport and are predominantly inorganic. The inorganic (PIP) and organic (POP) fractions of the TPP loads represent 20–47% and 6–28% of the annual TP transport, respectively. In contrast, the particulate nitrogen loads (TPN) represent 8% or less of the annual total nitrogen (TN) loads and are predominately organic. For dissolved P transport, the dissolved inorganic fraction (DIP) is more important, representing 15–70% of the TP loads, whereas the dissolved organic fraction (DOP) represents only 3–9% of the TP loads. The TN loads are dominated by the dissolved component and more particularly the total oxidized fraction (TON), which is composed of nitrate and nitrite and represents 76–82% of the annual TN transport. The remaining dissolved N species, ammonium (NH₄-N) and organic N (DON) account for 0·3–1·2% and 13–16% of the annual TN transport, respectively. The TPN and TPP fluxes closely reflect the suspended sediment dynamics of the study basins, which are in turn controlled by basin size and morphology. The dissolved inorganic nutrient fluxes are influenced by point source inputs to the study basins, especially for P, although the TON flux is primarily influenced by diffuse source contributions and the hydrological connectivity between the river and its catchment area. The dissolved organic fractions are closely related to the dissolved organic carbon (DOC) dynamics, which are in turn influenced by land use and basin size. The magnitude of the NH₄-N fraction was dependent on the proximity of the monitoring station to point source discharges, because of rapid nitrification within the water column. However, during storm events, desorption from suspended sediment may be temporarily important. Both the magnitude and relative contribution of the different nutrient fractions exhibit significant seasonal variability in response to the hydrological regime, sediment mobilization, the degree of dilution of point source inputs and biological processes. © 1998 John Wiley & Sons, Ltd.     

崇明东滩沉积物磷的分布特征及环境意义

对崇明东滩采集的表层样和柱状样品,进行样品的总磷(TP)、无机磷(IP)和有机磷(OP)以及有机质含量等的测定,分析了磷的分布变化特征并对其影响因素和环境意义进行了探讨。     

乌梁素海沉积物中全磷的分布特征

开展了浅水草型湖泊乌梁素海沉积物中TP(全磷)的分布特征研究。结果表明,乌梁素海表层沉积物中TP含量在0.37~0.99 g/kg之间变化,平均值为0.75 g/kg;水平分布上,TP含量呈现从湖区四周向湖心递减的变化趋势,大部分湖区已具有生态毒性效应,并对湖区底栖生物群落和生态环境构成了较大威胁;垂向上,尽管沉积物中TP含量有所波动,但0~10 cm的表层沉积物中TP含量均随深度增加而递减,揭示了近年来人类活动的加剧对乌梁素海沉积物中磷累积的重大影响;实验得出了粉砂、粘土粒级>极细砂粒级>细砂粒级>中砂以上粒级的TP含量序列,各粒级对TP的吸附贡献率由吸附能力和质量百分比共同控制;磷的沉积对乌梁素海富营养化进程有深远影响。     

1988-2018年滇池氮磷比的时空演变特征与原因解析

氮、磷浓度是制约湖泊营养状态和生产力水平的重要环境因子,而氮磷化学计量比是湖泊生态系统的主要指标,因此,判识氮磷比变化趋势及其驱动力对湖泊生态恢复具有重要意义.研究基于19882018年连续观测数据,分析了滇池氮磷浓度和氮磷摩尔比(简称氮磷比)的时空分布演变特征;采用多元线性回归模型分别对滇池草海和外海氮磷比驱动效应进行定量解析,筛选出影响湖体氮磷比变化的潜在驱动因子.结果表明:①19882018年滇池氮磷比呈现显著的线性上升趋势,其中草海和外海氮磷比分别上升1.3和0.7 a^-1.②草海和外海分别在2008年和2004年发生了氮磷比上升突变,突变前上升归因于总氮浓度快速增加,突变后则是由于总磷浓度下降较快.③滇池的氮磷浓度变化主要是受流域氮磷输入负荷、跨流域调水、流域氮磷削减、风速和水位的综合影响,但受控因子在不同区域可能存在差异.④气温是滇池氮磷比变化的主要驱动因子,流域人为氮磷输入差异是滇池氮磷比变化的次要驱动因子.