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1.
风浪扰动引起湖泊磷形态变化的模拟试验研究   总被引:8,自引:0,他引:8       下载免费PDF全文
为了解一次完整的大风浪过程(包括风浪扰动及扰动后的静风期)水体中各形态磷的变化情况及其影响因素,进行了室内模拟风浪扰动的试验研究。结果显示大风浪扰动初期水体中悬浮物(SS)、总磷(TP)、颗粒态磷(PP)和溶解性总磷(DTP)的浓度大幅增加,扰动持续半天后水体SS、TP、PP的浓度均达到最大值,扰动停止后,至少需要10d时间水体中SS、TP、PP的浓度才能回复到扰动前水平;扰动期间水体DTP浓度居于高值,但风浪停止后立即降低;整个风浪过程水体中溶解性反应磷(SRP)浓度变化不大。试验表明,扰动初期沉积物中Fe、Mn结合态磷能快速释放到水体中,但随着扰动的持续,水体复氧,释放到水体中的溶解性活性磷又能与Fe、Mn结合随悬浮物沉降到水底。扰动期间及随后静置1d时间内,水体中悬浮颗粒物的中值粒径连续下降,意味着悬浮颗粒物对磷的吸附能力在不断增强。但水体静置较长时间后,扰动引起的悬浮物几乎全部沉降,絮凝等作用导致水体颗粒物粒度增大。本研究说明虽然大风浪扰动初期能引起浅水湖泊中颗粒态和溶解态营养盐浓度的迅速提高,能够为水华蓝藻的快速生长提供大量可直接利用或酶解的营养盐,但随着风浪扰动的持续,由于水体复氧、水中颗粒物粒度不断细化、颗粒物中的有机成分比例不断增高等,悬浮颗粒物对活性磷的吸附能力也相应提高,两种作用相互削减使得风浪扰动后期水体活性磷浓度的增幅并不明显。  相似文献   

2.
密云水库沉积物-水界面磷的地球化学作用   总被引:11,自引:4,他引:11  
以密云水库为例,研究了水库沉积物中有机质的含量与有机磷的关系,表明表层沉积物中的总有机碳和有机磷的含量都明显高于底层,是由于一些以磷为营养素的富营养化指示藻类在水体中逐年增加,它们死亡后的残骸经分解-矿化后在底积物中累积的结果。沉积物和孔隙水中磷的剖面特征研究表明,表层沉积物和孔隙水中的磷都有明显上升的趋势,是由于沉积物的表层微生物和活性有机碎屑层比较丰富,有机质降解和含磷的有机化合物分解,使溶解性磷酸盐进入孔隙水。对沉积物磷形态、总有机碳及孔隙水中总磷对磷释放的影响进行了线性相关分析,结果表明上覆水中的磷主要来自沉积物的铁结合态磷、铝结合态磷、溶解态磷三种形态,孔隙水中总磷以及总有机碳含量对上覆水中总溶解磷浓度存在较大的影响,这些为研究水库沉积物作为水库内污染源对水质的影响提供了基础资料。  相似文献   

3.
强弱风浪扰动下太湖的营养盐垂向分布特征   总被引:24,自引:4,他引:24       下载免费PDF全文
在一次风速12m/s的强风浪过程中及在连续多天弱风浪之后,对太湖梅梁湾一浅水区营养盐、悬浮物等的垂向分布进行了观测和分析。结果表明,在水底沉积物约20cm的情况下,强风浪期间与弱风浪期间相比,湖水中悬浮物浓度提高了10倍,总磷浓度提高了3 6倍。而强风浪期间与弱风浪期间的水体溶解性总磷(DTP)、溶解性活性磷(SRP)的浓度无显著差异。说明尽管强风浪过程引起沉积物大量悬浮,水体悬浮颗粒态营养盐显著增高,但是由于悬浮过程营养盐释放与沉降机制作用十分复杂,活性营养盐的浓度未必能提高。无论强风浪还是弱风浪期间,水体的表层至水土界面上50cm层的悬浮物浓度、营养盐浓度没有明显的分层现象,但明显低于水土界面上50cm内的悬浮物浓度和总磷浓度。无论是强风浪期间还是弱风浪期间,表层到底层水体SRP浓度无显著差异。  相似文献   

4.
水体中富营养化水平与磷元素的赋存形态密切相关。目前围绕引起富营养化关键因子之一的磷形态的垂向分布特征、各磷形态间的迁移转化行为及其影响因素取得了比较明确的研究进展。为进一步揭示不同磷形态在沉积物-水体系中迁移转化行为随时空的变化特征,本文采用磷钼蓝分光光度法对沱江流域简阳段间隙水中可溶性活性磷(SRP)、可溶性非活性磷(SUP)及总溶解性磷(TDP)进行测定;采用SMT法和改进的沉积物无机磷形态连续提取法对沉积物中总无机磷(TIP)、总磷(TP)、难提取磷(Res-P)、可交换态磷(Exc-P)、铁结合态磷(Fe-P)、铝结合态磷(Al-P)、钙结合态磷(Ca-P)进行提取,磷钼蓝分光光度法进行测定,以揭示沉积物-水体系中磷的赋存形态垂向分布行为特征,并将实验数据与十年前该地区磷的赋存形态结果进行对比,探讨磷赋存形态的变化趋势及影响因素。结果表明:间隙水中SRP、SUP和TDP的含量分别为0.004~0.36mg/L、0.080~3.19mg/L和0.056~3.28mg/L;沉积物中TP、TIP、Res-P、Exc-P、Al-P、Ca-P含量分别为1235.40~1646.94mg/kg、860.00~1318.59mg/kg、130.31~537.13mg/kg、1.35~14.10mg/kg、0.007~0.12mg/kg、743.13~1109.91mg/kg,Fe-P未检出。对比十年前后沉积物-水体系中磷赋存形态的变化可知,由于受到外源磷输入的影响,间隙水中SRP、SUP以及TDP含量虽然在-10cm以上变化不明显,但在-10cm以下明显增大,且导致沉积物中TP、TIP含量增加;偏碱性的沉积环境导致Al-P的释放,其含量明显减小;Exc-P含量的减小与其转化为稳定的Ca-P或Res-P形态有关。研究认为:随着时空的变化,沱江简阳段沉积物呈现外源磷输入和内源磷释放的综合污染。总体而言,由于输入的磷形态大部分以稳定的Ca-P和Res-P形态存在于沉积物中,使得表层间隙水中生物可直接利用的磷含量总体变化不大,该地区富营养化程度不会加重。维持沉积环境的弱碱性,有利于Al-P、Exc-P等向Ca-P的有效转换,抑制河流富营养化。  相似文献   

5.
平水期洞庭湖不同形态磷赋存特征   总被引:4,自引:0,他引:4       下载免费PDF全文
王丛丹  汪金成  杨宇  钱宝  杨朝云  阎梅 《水文》2019,39(6):74-79
通过现场调查和室内实验,对平水期洞庭湖24个断面上覆水-沉积物磷的污染程度、分布特征进行研究;同时,分析了各形态磷间的相关性,探讨了磷的赋存形态对水体富营养化的影响、沉积物释放量和释放风险。结果表明,水体内总磷分布规律为南洞庭西洞庭东洞庭大通湖,东洞庭湖以颗粒态磷为主,西洞庭湖、南洞庭湖、大通湖均以溶解态磷、无机磷为主。沉积物中总磷的分布规律为南洞庭西洞庭东洞庭大通湖。东洞庭湖、西洞庭湖、南洞庭湖则以Ca-P为主,大通湖以Fe/Al-P为主。Ca-P与Fe/Al-P呈现较显著的负相关关系。大通湖释放风险较大,可释放量大;东洞庭湖有一定的可释放量,应对这两个湖泊给予较多的关注。与国内其他湖泊比较,洞庭湖沉积物中TP处于中下水平,IP在沉积物中占据较高比例。湖区沉积物中Fe/Al-P与水体中DIP、DTP、TP均具有较显著的负相关关系,存在磷的内源释放。  相似文献   

6.
太湖入湖河道沉积物中生物利用磷和营养水平分析   总被引:7,自引:0,他引:7  
为了解太湖入湖河道的营养状况,研究了太湖西部河流沉积物生物利用磷的组成与分布。研究结果显示,北部沉积物中营养元素较高,南部较低;沉积物中生物利用磷的含量次序为藻类可利用磷(AAP)>NaHCO3提取磷(OLP)>水溶性磷(WSP)>易解吸磷(RDP),其中AAP是重要的生物利用磷,AAP的比例越高,富营养化程度越高。AAP与营养元素的相关性在不同区域河道有所不同,北部河道与总氮(TN)、总磷(TP)相关性较好,中部和南部河道与沉积物有机质总量(TOM)相关性较好。沉积物的生物利用磷受不同污染源影响较大。对比河道沉积物与湖泊沉积物的特征,发现湖泊沉积物中生物利用磷(BAP)/总磷(TP)、藻类可利用磷(AAP)/总磷(TP)都高于河道沉积物,表明湖泊沉积物中的磷更容易被植物吸收。  相似文献   

7.
沉水植物黑藻对沉积物磷吸附动力学的影响   总被引:4,自引:0,他引:4  
在室内模拟条件下,通过吸附动力学实验,研究了沉水植物黑藻对沉积物吸附磷动力学模型拟合和吸附速度的影响,并从有机质和铁铝氧化物含量的角度,讨论了沉水植物黑藻对沉积物吸附磷动力学的影响机理。初步得出如下结论:(1)一级反应动力学模型虽然从模型拟合的角度达到了极显著水平,但不能真实地反映沉水植物对沉积物吸附磷动力学过程的影响。其余三个模型均能很好地反映,其中抛物线扩散模型的拟合效果最好,修正的Elovich模型和双常数速率模型的拟合效果较好。种植沉水植物与否并不影响这一趋势;(2)沉水植物黑藻提高了沉积物吸附磷的强度和速度,特别是提高了0~0.5h内的吸附速度,沉水植物影响有机质和铁铝氧化物含量是增强沉积物吸附磷强度和速度的重要机理。  相似文献   

8.
为了控制水体富营养化,对沉积物中磷的分布特征进行了研究。在海河干流采集13个表层沉积物和表层水样,采用逐级提取法获得可交换态磷(NH4Cl-P)、可还原态磷(BD-P)、铁铝结合磷(NaOHP)、钙磷(HCl-P)和残渣态磷(Res-P),分析各形态磷空间分布及其对水相(间隙水、表层水)磷的影响。结果表明:海河干流表层沉积物中总磷质量分数较高,为808.5~1 698.7mg·kg-1,上游和下游的采样点含磷量较低,中游采样点含磷量较高;不同形态磷的质量分数差异较大,NH4Cl-P、BD-P、NaOH-P、HCl-P和Res-P的质量分数变化范围分别为8.1~31.1、41.9~84.9、151.6~348.2、312.2~819.9、226.8~1 003.0mg·kg-1,分别占总磷(TP)的0.65%~1.85%、3.19%~6.57%、10.8%~24.34%、20.26%~52.18%、24.41%~58.33%;间隙水中总溶解性磷与沉积物中NH4Cl-P、BD-P、NaOH-P的质量分数相关性较高,相关系数分别达到0.892、0.848、0.749。研究结果表明海河内源磷释放的主要控制方向为NH4Cl-P、BDP、NaOH-P。  相似文献   

9.
采集了7组滇池近代沉积物柱芯,测定了其中总P(TP)、Fe、Al、Ca的含量,并首次获得了埋深大于25 cm的沉积物的不同形态磷的数据,分析了TP与不同形态磷的时空分布特征及TP与总Fe、Al、Ca含量的关系,探讨了滇池内源磷释放潜力的区域差异和制约因素。结果表明,自北向南,TP含量出现随深度先升高后降低的变化特征,各形态P之间的关系为:碎屑磷(DP)>有机磷(OP)≈铁结合态磷(Fe-P)>闭蓄态磷(Oc P)>钙结合态磷(Ca-P)>铝结合态磷(Al-P)>可交换态磷(SRP)。纵向上Fe-P随深度逐渐升高,Oc P逐渐降低,其它形态P的变化规律不明显;区域上TP、DP、OP、Fe-P、Ca-P和Al-P南部高于北部。在滇池南部DP通量较高的区域,TP与Fe、Al呈正相关关系,与Ca呈负相关关系,其它区域无相关性。分析表明,滇池南部内源磷的释放潜力大于中部和北部,而南部内源磷受DP输入的影响,风浪扰动对北部内源磷的释放有更强的抑制作用。  相似文献   

10.
三峡库区消落区表层沉积物磷吸附特征   总被引:2,自引:0,他引:2       下载免费PDF全文
以三峡库区消落区表层沉积物为研究对象,通过对干湿交替沉积物中磷的赋存形式、吸附等温曲线的分析,揭示了干湿交替过程中沉积物磷的分布规律、吸附特征以及磷的源汇变化。结果表明:上覆水总磷变化呈现11月总磷<5月总磷<8月总磷。消落区覆水到出露沉积物最大磷吸附量、土壤最大缓冲能力在增加,磷零吸持平衡浓度、易解吸磷在降低,表明沉积物在夏季出露落干的过程中,固磷能力增强,释磷能力减弱;消落区土壤首次覆水过程中土壤磷呈现出由源到汇的转变。成库初期,覆水时沉积物主要表现为磷的积累,次年水库开闸放水排沙时,消落区表层富磷沉积物被冲刷排出。  相似文献   

11.
河岸带土壤磷素空间分布及其对水文过程响应   总被引:2,自引:0,他引:2       下载免费PDF全文
野外观测太湖地区典型农业河岸带——浯溪荡河岸带土壤总磷(TP)和溶解性总磷(DTP)含量以及当地降雨量、河水水位和地下水水位,探讨了丰水年条件下该河岸带土壤TP和DTP的空间分布特征以及水文过程对其空间分布的影响。结果表明:①在水平方向上,土壤TP和DTP含量从远岸向近岸均呈现先减少后增加的变化趋势;在深度方向上,各断面TP和DTP含量随土层深度的增加均呈减少的变化趋势。②不同月份河水水位均低于地下水水位,地下水补给河水。河水水位和地下水水位随时间的变化规律与降雨量的相似,但具有一定的滞后性。③降雨是土壤水分运动的主要驱动力,降雨、河水水位以及地下水水位对河岸带土壤磷素空间分布的影响显著不同。  相似文献   

12.
This study was designed to investigate non-point source nutrient pollution and its influences on submerged aquatic plant community structure and biological invasion in the Weeks Bay National Estuarine Research Reserve (WBNERR). A monthly vegetation survey was conducted to document plant abundance and changes in community structure; physicochemical data and water samples were collected on a bi-monthly basis to monitor environmental conditions (i.e., pH, salinity, dissolved oxygen, light intensity, and attenuation) and water column nutrient (NO2/NO3 and NH4+) and chlorophyll a concentrations. A total of seven submerged aquatic species were identified at the WBNERR with the occurrence of only one non-native species (Hydrilla verticillata). Statistical analyses suggest that water column nitrogen concentrations along with variations in dissolved oxygen (0.6–11.5 mg L−1), light attenuation, pH (5.6–8.6), and temperature (11–33°C) play key roles in determining the aquatic plant abundance and distribution in the WBNERR.  相似文献   

13.
The effects of inactivation agents, including common polymeric aluminium (Al) chloride (CPAC) and Ecological Type PAC (UNIC), on phosphorus (P) released from sediment are unclear. To determine these effects, we performed seven experiments using various inactivation agent additions. The experimental schemes used were as follows: (1) CPAC, 15 mg Al L?1; (2) CPAC (15 mg Al L?1) + polyacrylamide (PAM) (0.5 mg L?1); (3) UNIC, 5 mg Al L?1; (4) UNIC, 15 mg Al L?1; (5) UNIC, 60 mg Al L?1; (6) control set without any inactivation agent addition; and (7) alkali shock load (the pH value of overlying water in the scheme 7 was adjusted to 11 by addition of sodium hydroxide to simulate alkali shock load at 13 days after CPAC addition). The experiments were conducted in glass columns, each containing 0.3 L sediment from Lake Dianchi and 3 L of overlying water. The results showed that P release rate decreased as the amount of inactivation agent added increased. P release rate was calculated according to each inactivation agent and the amount of inactivation agent added. Release rate found was in the decreasing order: (6) > (3) > (4) > (1) > (5) > (2). The corresponding rate was calculated to be 7.11, 6.16, 4.55, 1.76, 1.46 and 1.00 mg P m?2 day?1, respectively. Dissolved total P (DTP) was the main form of total P (TP) in the overlying water. After the addition of PAM, the DTP:TP ratio decreased while the dissolved inorganic P (DIP):DTP ratio increased. With increasing the amount of inactivation agents added, both DTP:TP and DIP:TP ratios decreased. Experimental group 3 had similar DTP:TP and DIP:TP ratios to experimental group 6. These results are significant in terms of the large-scale application of inactivation agents for reducing levels of bioreactive P. Alkali shock load (experimental group 7) caused failure in the inactivation of P by CPAC.  相似文献   

14.
Benthic fluxes of soluble reactive phosphorus (SRP) and dissolved inorganic carbon (DIC) were measured in situ using autonomous landers in the Gulf of Finland in the Baltic Sea, on four expeditions between 2002 and 2005. These measurements together with model estimates of bottom water oxygen conditions were used to compute the magnitude of the yearly integrated benthic SRP flux (also called internal phosphorus load). The yearly integrated benthic SRP flux was found to be almost 10 times larger than the external (river and land sources) phosphorus load. The average SRP flux was 1.25?±?0.56?mmol?m?2?d?1 on anoxic bottoms, and ?0.01?±?0.08?mmol?m?2?d?1 on oxic bottoms. The bottom water oxygen conditions determined whether the SRP flux was in a high or low regime, and degradation of organic matter (as estimated from benthic DIC fluxes) correlated positively with SRP fluxes on anoxic bottoms. From this correlation, we estimated a potential increase in phosphorus flux of 0.69?±?0.26?mmol?m?2?d?1 from presently oxic bottoms, if they would turn anoxic. An almost full annual data set of in situ bottom water oxygen measurements showed high variability of oxygen concentration. Because of this, an estimate of the time which the sediments were exposed to oxygenated overlying bottom water was computed using a coupled thermohydrodynamic ocean?Csea and ecosystem model. Total phosphorus burial rates were calculated from vertical profiles of total phosphorus in sediment and sediment accumulation rates. Recycling and burial efficiencies for phosphorus of 97 and 3%, respectively, were estimated for anoxic accumulation bottoms from a benthic mass balance, which was based on the measured effluxes and burial rates.  相似文献   

15.
An urban stream differs from a natural stream in that it commonly contains anthropogenic nutrients from a variety of diffuse and point sources (e.g., urban runoff, industrial and municipal effluents). The Cuyahoga River as one of such stream systems receives on average 30% of water from over a dozen wastewater treatment plants (WWTPs) and exports over 300 Mg/yr of total phosphorus (TP) into Lake Erie. Municipal effluents account for at least two thirds of the TP loading and 90% of the effluent TP is in the form of soluble reactive phosphorus (SRP), i.e., the highly bioavailable form in aquatic ecosystems. Owing to its dominance of the effluent P, the Cuyahoga River may pose a disproportionately greater ecological risk to Lake Erie. Here we report results of TP and SRP as measured on water samples collected from 12 locations along the Cuyahoga River and its major tributary – Tinkers Creek under three different flow conditions in July 2007 through May 2008. Our results show that the loadings of SRP and TP increased progressively with the effluent inputs increasing from the upper basin downstream. We found the loadings of SRP and TP are not only affected by the amount of effluent P input but also regulated by stream flow regimes. Effluent P is more likely to be transformed during storm runoff events, whereas TP is more likely to be retained under low flow conditions. As a result, most of the TP loading was exported during the storm and intermediate flow conditions, whereas most of the SRP loading was delivered during the low and intermediate flow conditions. These results suggest that stream hydrology has played an important role in the loading and transport of P across the Cuyahoga River as it dictated the amount, form, and timing of P exported to Lake Erie.  相似文献   

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