Phosphorus speciation in the sediment profile of Lake Erhai, southwestern China: Fractionation and 31P NMR

The distribution characteristics of phosphorus(P) forms in the sediment profile of Lake Erhai,in southwestern China has been investigated by sequential extraction and 31P nuclear magnetic resonance spectroscopy(NMR) of NaOH extracts to understand P dynamics and its potential contribution to lake eutrophication.Contents of P fractions varied in the order of NH4Cl extracted P(NH4ClP) < bicarbonate-dithionite extracted P(BD-P) < HCl-P,Residual-P < NaOH extracted P(NaOH-P).The highly available NH4Cl-P represented less than 1% of total P(TP).BD-P and NaOH extracted reactive P(NaOH-rP) averaged 39%,while the ratio of Fe/P was higher than 15,indicating low P release from the sediments under permanent oxic condition.The less bio-available HCl-P,NaOH extracted nonreactive P(NaOH-nrP) and residual-P contributed 61% of TP.Regression analysis revealed that BD-P,NaOH-rP and HCl-P were positively correlated with the contents of Fe and Mn,Al and Fe,and Ca,respectively.The investigation of P compound groups in NaOH extracts by 31 P NMR showed that ortho-P and monoester-P were the largest two constituents of the P pool,followed by diester-P,phosphonate and pyro-P.A comparison of vertical variations of P groups in the sediment profile suggested that these compounds were involved in the P recycling to different extents in Lake Erhai.In particular,the lake exhibits high potential for labile P release from the surface sediments,which should be taken into consideration even after the outsourced P runoff ceased.     

Characteristics and distribution of phosphorus in surface sediments of a shallow lake

Phosphorus ( P ) in sediments plays an important role in shallow lake ecosystems and has a major effect on the lake environment. The mobility and bioavailability of P primarily depend on the contents of different P forms, which in turn depend on the sedimentary environment.Here, sediment samples from Baiyangdian (BYD) lake were collected and measured by the Standards, Measurements, and Testing procedure and Phosphorus-31 nuclear magnetic resonance spectroscopy (31P NMR) to characterize different P forms and their relationships with sediment physicochemical properties. The P content in the sediments varied in different areas and had haracteristics indicative of exogenous river input. Inorganic P (334–916 mg/kg) was the dominant form of P . The 31P NMR results demonstrated that orthophosphate monoesters (16–110 mg/kg), which may be a source of P when redox conditions change, was the dominant form of organic P (20–305 mg/kg). The distribution of P forms in each region varied greatly because of the effects of anthropogenic activities, and the regions affected by exogenous river input had a higher content of P and a higher risk of P release. Principal component analysis indicated that P bound to Fe, Al, and Mn oxides and hydroxides (NaOH-P) and organic P were mainly derived from industrial and agricultural pollution, respectively. Redundancy analysis indicated that increases in pH lead to the release of NaOH-P. Organic matter plays an important role in the organic P biogeochemical cycle, as it acts as a sink and source of organic P .     

滇池与红枫湖沉积物中磷的地球化学特征比较研究

对比研究了滇池与红枫湖表层沉积物中磷的形态含量及其生物有效性.结果表明,两湖沉积物总磷含量相当,分别为1373.8～ 4616.3mg·kg-1、1194.4 ～4324.3 mg·kg-1.HCl-P、Res-P为滇池沉积物中主要的磷形态,占总磷的62.9％ ～86.4％;而红枫湖中磷形态顺序为NaOH-P＞ Res-P＞ HCl-P＞ BD-P＞ NH4Cl-P;两湖沉积物中有机磷均以低活性态为主.红枫湖沉积物中NH4Cl-P、BD-P、NaOH-rP及生物有效磷等平均含量明显高于滇池,表明其内源磷释放对上覆水体富营养化的贡献更大.Olsen-P与NH4Cl-P、BD-P、NaOH-rP等活性磷形态呈显著正相关,而与NaOH-nrP、HCl-P、Res-P、TP等相关性不显著,因此,可作为评价两湖沉积物释磷能力及其潜在环境风险的重要指标.     

Biogenic silica in intertidal marsh plants and associated sediments

Biogenic silica (BSi) contents in the marsh plants (Phragmites australis, Scirpus mariqueter and Spartina alterniflora) and associated sediments in Chongming Island eastern intertidal flat of the Yangtze Estuary were determined. The BSi contents in P. australis, S. mariqueter and S. alterniflora varied from 25.78–42.74 mg/g, 5.71–19.53 mg/g and 6.71–8.92 mg/g, respectively. Over the entire growth season, P. australis and S. mariqueter were characterized by linear accumulation patterns of BSi. The aboveground biomass (leaves and culms) of the marsh plants generally contained more BSi than underground biomass (roots). BSi contents were relatively higher in dead plant tissues than in live tissues which was probably due to the decomposition and the leaching of labile components of plant tissues such as organic carbon and nitrogen. Comparing with the habitats of S. mariqueter and S. alterniflora, the highest BSi content was recorded in sediments inhabited by P. australis, with an annual average of 15.69 mg/g. Overall, the intertidal marshes in the Yangtze Estuary may act as a net sink of BSi via plant uptake and sedimentary burial.     

Catchment soils as a factor of trace metal accumulation in sediments of the reservoir Klingenberg (eastern Ore Mountains, Germany)

The release and accumulation dynamics of trace metals in soils and aquatic sediments were exemplarily investigated in the catchment area of the Reservoir Klingenberg(Germany). Catchment soils were examined for mobilizable and total concentrations of arsenic(As), cadmium(Cd), chrome(Cr), iron(Fe), manganese(Mn), nickel(Ni), lead(Pb),and zinc(Zn) and compared with trace metal quantities accumulated in riverbed and reservoir sediments. The comparison of all samples showed relatively small variations of Cr(7.96–46.0 mg/kg), Fe(7.79–40.4 g/kg), and Ni(6.06–56.5 mg/kg), while stronger differences were found for As(11.2–164 mg/kg), Cd(0.14–30.5 mg/kg), Mn(0.08–1.84 g/kg), Pb(20.7–183 mg/kg), and Zn(69.1–916 mg/kg). The catchment soils were slightly enriched by Cd, Pb, and Zn. Especially Cd and Zn were characterized by large mobilizable proportions.The mean trace metal concentrations in riverbed sediments were higher than in catchment soils, while reservoir sediments accumulated the highest amounts of the analyzed elements. The enrichment of trace metals in reservoir sediments was generally determined by the sedimentation of fine particles, while the distribution of As, Fe, and Mn was additionally impacted by redox conditions. For Cd and Zn, which in comparison were most enriched in riverbed and reservoir sediments, a significant release from soils by leaching processes was observed. The accumulation of As and Pb in reservoir sediments was influenced to a greater extent by soil erosion and by anthropogenic or chalcogen sources in the catchment.     

Phosphorus accumulation and eutrophication in feed-supply freshwater fishponds

The rapid growth and intensification of freshwater fishery can cause imbalances between phosphorus （P） input in feed and its output in produce. This aquaculture can result in enriching exogenous P in fishponds and, consequently, accelerates the process of eutrophication. To assess relations among input, accumulation, release of P and as a consequence degrading water quality in terms of chlorophyll-a （Chl-a） in freshwater fishponds, fourteen fishponds with feed supply, nine fishponds without feed supply, and five nonfish ponds in Shaoxing Plain, southeast China were selected for comparing P accumulation in their waters and surface sediments. Surface sediment samples were collected from each pond to evaluate their total P, water soluble P, Olsen P, algal available P, and P fractions. Water samples were also collected from the ponds to measure concentrations of dissolved P and Chl-a. Total P in the sediments ranged from 0.88 to 1.73 g/kg in the fishponds with feed supply, that in the non-fish ponds ranged from 0.47 to 0.86 g/kg. Organic P, accounted for 23% to 60% of total P in the sediments, was an important P fraction and increased linearly with increasing organic matter. Long-term application of feeds resulted in increased P availability in the bottom sediments and degradation of water quality in the freshwater fishponds. Compared with non-fish ponds, sediments from the feed-supplied fishponds contained considerably higher Olsen P, algal available P, and water soluble P. Higher proportions of the labile P （NH4Cl-P） and potentially labile P （NaOH-IP） were also found in the sediments from the fishponds. High solubility of P in the sediments resulted in elevation of P and chlorophyll-a concentration in the pond water. The dissolved P concentration in the pond water increased in the order of non-fish ponds （12μg/L） 〈 fishponds without feed supply （24 μg/L） 〈 fishponds with feed supply （66 μg/L）. Linear correlations between concentrations of total P, Olsen-P, algal available P, water-soluble P and P concentration in saturation extracts in the sediments and dissolved P in the pond water indicated that there was a buffering action of the sediment constituents on the dissolved P.     

Fraction distribution and risk assessment of heavy metals in sediments of Moshui Lake

To examine the status and risk of heavy metal pollution in urban lakes, in China, the distribution of several heavy metals (e.g., Cr, Cu, Ni, Pb, Zn) in the sediment of Moshui Lake, Hangyang District, Wuhan City, was characterized. The process of rapid urbanization and industrialization of the district was also studied to find out its relationship with the metal accumulation profile in the sediment. It was found that the total concentration of heavy metals in the sediment was higher than the severe e ect level (SEL), at all sampling sites, except those in the riparian zone. The Cr and Cu maximum concentrations were 1,780 and 1,250 mg/kg, approximately 16 and 11 times as much as the SEL values, and they appeared as deep as 32 cm in one sample. The carbonate and exchangeable fractions of Zn were more than 50% of the total Zn content, resulting in very high risk according to the Risk Assessment Code (RAC). For Cu and Ni, a medium RAC value was found for carbonate and exchangeable fractions of 11%–20%. As sensitive indicators of contaminants in aquatic systems, heavy metals in the sediment reflect the outcome of regional urbanization, industrialization, and environmental management. With rapid urbanization, sedimentary Pb and Zn concentrations increased. The experimental results showed that high sedimentary heavy metal concentrations had resulted from rapid urbanization and industrialization, which would absolutely lead to substantial aquatic environmental decline in urban lakes.     

Rates and processes affecting As speciation and mobility in lake sediments during aging

Sediments from an arsenic(As) contaminated groundwater vent site were used to investigate As( Ⅲ) binding, transformation and redistribution in native and iron oxide amended lake sediments using aging spiked batch reactions and a sequential extraction procedure that maintains As(V) and As( Ⅲ) speciation. In the native sediments, fractionation analysis revealed that 10% of the spiked As( Ⅲ) remained intact after a 32-day aging experiment and was predominantly adsorbed to the strongly sorbed(NH_4H_2PO_4 extractable) and amorphous Fe oxide bound(H_3PO_4 extractable) fractions. Kinetic modelling of the experimental results allowed identifying the dominant reaction path for depletion of dissolved As( Ⅲ) to As( Ⅲ)absorbed on to the solid phase, followed by oxidation in the solid phase. Arsenite was initially adsorbed primarily to the easily exchangeable fraction((NH_4)_2SO_4 extractable), then rapidly transformed into As(V) and redistributed to the strongly sorbed and amorphous Fe oxide bound fractions. Oxidation of As( Ⅲ) in recalcitrant fractions was less efficient. The iron oxide amendments illustrated the controls that iron oxides can have on As( Ⅲ) binding and transformation rates. In goethite amended samples As( Ⅲ) oxidation was faster and primarily occurred in the strongly sorbed and amorphous Fe oxide bound fractions. In these samples,19.3 μg Mn was redistributed(compared to the native sediment) from the easily exchangeable and crystalline Fe oxide bound fractions to the strongly sorbed and amorphous Fe oxide bound fractions, indicating that goethite may act as a catalyst for Mn(Ⅱ) oxidation, thereby producing sorbed Mn( Ⅲ/Ⅳ ), which then appears to be involved in rapidly oxidizing As( Ⅲ).     

Phosphate removal from domestic wastewater using thermally modified steel slag

This study was performed to investigate the removal of phosphate from domestic wastewater using a modified steel slag as the adsorbent. The adsorption effects of alkalinity, salt, water,and thermal modification were investigated. The results showed that thermal activation at 800℃ for 1 hr was the optimum operation to improve the adsorption capacity. The adsorption process of the thermally modified slag was well described by the Elovich kinetic model and the Langmuir isotherm model. The maximum adsorption capacity calculated from the Langmuir model reached 13.62 mg/g. Scanning electron microscopy indicated that the surface of the modified slag was cracked and that the texture became loose after heating. The surface area and pore volume did not change after thermal modification. In the treatment of domestic wastewater, the modified slag bed(35.5 kg) removed phosphate effectively and operated for 158 days until the effluent P rose above the limit concentration of 0.5 mg/L. The phosphate fractionation method, which is often applied in soil research, was used to analyze the phosphate adsorption behavior in the slag bed. The analysis revealed that the total contents of various Ca–P forms accounted for 81.4%–91.1%, i.e., Ca10–P 50.6%–65.1%, Ca8–P 17.8%–25.0%,and Ca2–P 4.66%–9.20%. The forms of Al–P, Fe–P, and O–P accounted for only 8.9%–18.6%. The formation of Ca10–P precipitates was considered to be the main mechanism of phosphate removal in the thermally modified slag bed.     

Phosphorus mobility in dam reservoir affected by redox oscillations: An experimental study

The internal sedimentary phosphorus(P) load of aquatic systems is able to support eutrophication, especially in dam–reservoir systems where sedimentary P stock is high and where temporary anaerobic conditions occur. The aim of this study therefore is to examine the response of sedimentary P exposed to redox oscillations. Surface sediments collected in the Champsanglard dam–reservoir(on the Creuse River, France) were subjected to two aerobic phases(10 and 12 days) alternated with two anaerobic periods(21 and 27 days)through batch incubations. The studied sediment contained 77 ± 3 μmol/g DW of P, mainly associated with the ascorbate fraction(amorphous Fe/Mn oxyhydroxides). The used sediment was rich in organic matter(OM)(21% ± 1%) with primarily allochthone signature.Our results showed that redox oscillations enhance dissolved inorganic phosphorus release at sediment/water interface. During the first anaerobic stage, the P release was mainly controlled by the dissolution/precipitation of iron minerals. The more pronounced increase of P release during the second anaerobic stage(44%) was due to various mechanisms related to the change in quality of dissolved organic matter(DOM), namely a higher SUVA254 and humification indices. The release of more refractory DOM(rDOM) served to lower the microbial metabolism activity, possibly favored iron oxyhydroxide aggregation and thus limiting iron reduction. In addition, rDOM is able to compete for mineral P sorption sites,leading to a greater P release. In reservoir with predominant allochthone OM input, the release of more aromatic DOM therefore plays an important role in P mobility.     

南水北调对密云水库水位变幅带土壤磷释放量的影响

南水北调来水引起的水位上涨可能会导致密云水库水位变幅带土壤中磷的释放.过量的磷可能会引起水体富营养,因此,研究水库变幅带磷释放风险对密云水库水质安全保障具有科学指导意义.本研究采用连续浸提法测定密云水库变幅带土壤及沉积物中弱吸附态磷(NH_4ClP)、铁磷(BD-P)、铝磷(NaOH-P)及钙磷(HCl-P)等4种不同形态磷含量,探讨其分布特征;并在室内进行了磷释放模拟实验,估算了南水北调来水引起水库水位上升所致的易释放磷的释放量.结果表明,NH_4Cl-P、BD-P、NaOH-P、HCl-P广泛地分布于密云水库变幅带土壤及沉积物中.在白河、内湖及潮河3个库区,磷形态分布具有一致规律,即HCl-PNaOH-PBD-PNH_4Cl-P.因密云水库变幅带为中国典型的北方碱性土壤,变幅带无机磷主要为钙磷.NH_4Cl-P在3个库区变幅带土壤中含量相差不大,在受水动扰动力影响较小的内湖库区BD-P含量略高于其它2个库区.在3个不同库区中,潜在活性磷NH_4Cl-P和较稳定的NaOH-P在岸上和水陆交界面土壤及水下沉积物中含量相差不大,受氧化还原条件影响较大的BD-P在沉积物中的含量略高于岸上和水陆交界面土壤.磷释放模拟实验及释放量估算结果表明,水库水位上涨3 m的情况下,白河、潮河和内湖库区淹没变幅带土壤分别释放1.02、0.80、0.37 mg·m~(-2)易释放磷.白河和内湖库区变幅带被水淹没土壤中磷释放的风险可能更高,需加强防护.     

Phosphorus fractionation and bio-availability in Taihu Lake(China) sediments

Introduction Sediment phosphorus has been recognized as the mostcritical nutrient limiting lake productivity (OECD, 1982).The concentration of phosphorus in the sediment is often1000 fold higher than that in lake water and its release…     

Characteristics of phosphorus fractionated from the sediment resuspension in abrupt expansion flow experiments

Phosphorous (P) fraction characteristics in sediment resuspension were investigated under adequately hydrodynamic conditions. Four forms of P in overlying water, including dissolved inorganic P, dissolved total P, total P, and particulate P, and six fractions of P in suspended particulate matter (SPM), including loosely sorbed P (NH4Cl-P), redox-sensitive P (BD-P), aluminum-bound P (Al- P), organic P (NaOH-nrP), calcium-bound P (Ca-P) and residual P (Res-P), were quantified, respectively. Di erent hydrodynamic conditions resulted in di erent P form changes. Four states could be ascribed: (1) P desorption by sediment and SPM, and P adsorption by overlying water; (2) P desorption by SPM, and P adsorption by overlying water; (3) P adsorption by SPM, and P desorption by overlying water; and (4) P equilibrium between SPM and overlying water. The contents of P in overlying water acquired peak values in the middle position of the vertical P distribution due to the combined actions of SPM and sediment. P fractions in SPM were in the following order: BD-P > NaOH-nrp > Ca-P > Al-P > Res-P > NH4Cl-P. BD-P in SPM frequently exchanged with P forms in overlying water. Resuspension was favorable to forming Ca-P in SPM.     

锆改性高岭土覆盖对底泥与上覆水之间磷迁移转化的影响

以无覆盖和高岭土覆盖作为对照,通过底泥磷释放控制模拟实验考察了厌氧条件下锆改性高岭土覆盖对重污染河道底泥与上覆水之间磷迁移转化的影响.结果表明,厌氧条件下,重污染河道底泥会释放出大量的磷进入上覆水中,且所释放出来的磷主要以溶解性磷酸盐为主.高岭土覆盖可以略微降低底泥磷向上覆水迁移的通量,而锆改性高岭土覆盖则可以极大降低底泥磷向上覆水迁移的通量.被高岭土覆盖层所吸附的磷中29%以氧化还原敏感态磷(BD-P)形式存在和63%以残渣态磷(Res-P)形式存在.被锆改性高岭土覆盖层所吸附的磷中绝大部分(90%)以金属氧化物结合态磷(NaOH-P)和Res-P形式存在,厌氧状态下很难被重新释放出来进入上覆水体.与无覆盖相比,厌氧条件下锆改性高岭土覆盖不仅不会促进底泥BD-P的释放,而且还会促进底泥NaOH-P的形成.X射线光电子能谱(XPS)和固相31P核磁共振(NMR)技术分析证实了锆改性高岭土覆盖层吸附水中磷酸盐的主要机制为配位体交换和形成内配合物.上述结果说明锆改性高岭土适合作为一种活性覆盖材料控制重污染河道底泥磷的释放.     

锆改性沸石添加对重污染河道底泥磷释放和钝化的影响

通过模拟实验并结合磷形态分级提取和生物有效磷提取,考察了锆改性沸石添加对重污染河道底泥磷释放和钝化的影响.结果发现,锆改性沸石添加不仅会降低间隙水中磷的浓度,而且也会降低底泥-水界面磷扩散通量,从而降低了底泥中磷向覆水体的释放风险.锆改性沸石添加会促使底泥中弱吸附态磷(NH_4Cl-P)、氧化还原敏感态磷(BD-P)和盐酸提取态磷(HCl-P)向金属氧化物结合态磷(NaOH-r P)和残渣态磷(Res-P)转变,而底泥中NH_4Cl-P和BD-P这2种容易释放态磷的降低有助于减少底泥中磷释放的风险.此外,锆改性沸石添加降低了底泥中了WSP(水溶性磷)、RDP(易解吸磷)、FeO-P(铁氧化物-滤纸提取磷)和Resin-P(阴离子交换树脂提取磷)这4种生物有效磷含量.锆改性沸石添加控制底泥磷释放的机制为:锆改性沸石添加,一方面可以钝化底泥中潜在可移动态磷和生物有效磷,达到减少底泥中磷向间隙水中释放的目的,另一方面可以通过锆改性沸石的吸附作用直接去除间隙水中的磷;而间隙水中磷浓度的降低,会降低间隙水和上覆水之间磷的浓度梯度,进而降低了底泥-水界面磷扩散通量.以上的结果显示,锆改性沸石是一种有希望的可以钝化河道底泥中磷并控制其向上覆水体释放的改良剂.     

淮南潘一矿塌陷水域沉积物中磷的赋存和迁移转化特征

采用改进的Pesnner分级提取方法,选取淮南潘一矿杨庄塌陷水域为研究对象,对其沉积物磷的剖面赋存形态进行分析,并结合磷的形态组成、有机质(OM)、总氮(TN)和铁锰氧化物等分布特征,研究了塌陷水域沉积物中磷的迁移转化特征.结果表明,在淹水农业耕作层上,湖泊沉积相累积明显,自表层而下,各形态磷含量均呈逐渐减少的趋势,总磷(TP)在各层次均值为204.9~343.7mg/kg,其中以无机磷(IP)为主,其含量为163.9~257.2mg/kg,占TP比例达73.3%~81.5%.NaOH-P(85.0~100.1mg/kg,28.6%~41.3%)和HCl-P (63.6~95.9mg/kg,27.4%~30.9%)所占比例较大.根据相关性结果分析,部分HCl-P和有机磷(OP)有向NaOH-P转化的趋势.     

镧改性沸石对太湖底泥-水系统中磷的固定作用

考察了不同反应时间、pH值、硅酸根离子浓度、DO浓度、老化时间以及初始磷浓度等条件下一种新型底泥改良剂-镧改性沸石对太湖底泥-水系统中磷的固定作用.当水中磷浓度很低时,太湖底泥和镧改性沸石改良太湖底泥均释放出磷.镧改性沸石改良太湖底泥的释磷量少于太湖底泥.镧改性沸石改良太湖底泥中金属氧化物结合态磷(NaOH-P)和钙结合态磷(HCl-P)等较为稳定形态磷含量多于太湖底泥,而镧改性沸石改良太湖底泥中氧化还原敏感态磷(BD-P)这种不稳定形态磷含量少于太湖底泥.太湖底泥和镧改性沸石改良太湖底泥对水中较高浓度磷酸盐的吸附平衡数据均可以采用Langmuir等温吸附模型加以描述.镧改性沸石改良太湖底泥对水中磷酸盐的吸附能力明显高于太湖底泥,且吸附能力随老化时间的增加而降低.被镧改性沸石所吸附的磷酸盐主要以NaOH-P和HCl-P等较为稳定形态磷存在,不容易被重新释放出来.上述结果表明,采用镧改性沸石对太湖底泥进行原位改良可以增强太湖底泥对磷的固定能力,减少太湖底泥磷的释放.     

底泥再悬浮状态下生物有效磷形成机制研究

研究了底泥再悬浮状态下,不同形态磷及生物有效磷(BAP)含量的变化,并对生物有效磷的形成机制进行了初步探讨.结果表明,底泥再悬浮对磷的赋存形态有显著的影响.随着底泥再悬浮时间的延长,铁结合态磷(BD-P),铝结合态磷(Al-P),钙结合态磷(Ca-P)含量显著增加,而弱吸附态磷(NH4C1-P)则有所减少.底泥再悬浮后, BAP平均下降6.59%,说明底泥再悬浮促进了 BAP 向难被生物利用态磷的转化.藻类可利用磷(AAP)主要来自BD-P,但提取AAP后,再悬浮底泥BD-P释放量平均下降了33.4%,而对照试验底泥BD-P释放量则增加了19,8%,说明BD-P的性质对AAP的形成有显著的影响;NaHCO,可提取磷 (Olsen-P)主要来自BD-P、Al-P 和 NaOH-nrP,按照三者的释放量, Olsen-P与BD-P的关系更为密切.     

苕溪干流悬浮物和沉积物的磷形态分布及成因分析

磷是控制水体营养状态和诱发富营养化的重要因素,不同形态的磷对水体富营养贡献不同.以东西苕溪干流为研究对象,采用连续提取法获得磷形态,对悬浮物和表层沉积物中磷形态的分布进行分析,并探讨了悬浮物和沉积物的物质组分与磷形态的相关性.结果表明,西苕溪水质状况劣于东苕溪,而东苕溪中游水体的水质状况好于上游和下游;悬浮物中营养物质含量普遍高于沉积物,其弱吸附态磷、还原态磷和金属氧化物结合态磷所占比例较表层沉积物大,钙结合态磷则在沉积物中占较高比例.相关性分析表明,西苕溪悬浮物和沉积物的组分对磷形态的影响较弱,而东苕溪的物质组分对磷形态有显著的影响,有机质和黏土矿物对悬浮物和沉积物中形态磷的影响最为显著,这与河流的地质背景及物质来源有关.