生活污水为主要补给源的城郊排水沟渠氮磷滞留特征

为揭示生活污水补给影响下排水沟渠氮、磷滞留特征,以合肥市城郊结合部的关镇河支渠为对象,以NH₄Cl和KH₂PO₄为添加营养盐,以NaCl为保守型示踪剂,开展5次现场示踪试验. 在此基础上,利用OTIS(one-dimensional transport with inflow and storage)模型估算D(扩散系数)、A(渠道过水断面面积)、A_s(暂态存储区断面面积)、α(暂态存储交换系数)、λ(主流区溶质一阶吸收系数)和λ_s(暂态存储区吸收系数);并利用营养螺旋原理,计算营养盐的S_w(吸收长度)、V_f(吸收速度)和U(吸收速率)等. 结果表明:①A_s/A具有随流量减小而增大的变化特征,平均值为0.35;5次试验得到的α均处在10-3数量级水平,平均值为2.49×10-3 s-1. ②S_w-NH₄和S_w-PO₄(分别表示NH₄-N和PO₄-P的S_w,下同)均较大,最大值分别达934 020、47 518 m,意味着关镇河支渠已基本不具备氮、磷滞留能力;而S_w-NH₄和S_w-PO₄均不同程度地出现负值,表明该支渠还具有“源”的作用. ③V_f-NH₄与河水平均深度、渠道流量均呈显著负相关,V_f-PO₄和U-PO₄与渠道水面宽度均呈显著正相关. ④NH₄-N和PO₄-P的营养螺旋指标与其相应质量浓度背景值无明显相关性.      

不同营养状态水体中生态浮床对浮游植物群落的影响

为研究不同营养状态下水体中浮游植物群落对生态浮床系统的响应关系及其影响因素,设不同营养水平试验组〔A组ρ(COD_Cr)、ρ(NH₄+-N)、ρ(TP)分别为10.0、2.00、0.200 mg/L,B组分别为100.0、20.00、2.000 mg/L〕,每组设对照、框式浮床2个处理,每个处理3个重复. 自2012年8月5日—10月5日,定期对水体营养盐质量浓度、浮游生物群落特征、浮床植物的生长状况进行检测. 结果显示:①2个试验组浮床植物长势良好,其中B组浮床植物茎叶部分干物质量增加7.9倍,浮床系统对水体N、P的净去除率均在60%以上;②浮床系统能明显抑制浮游植物的大量生长(P＜0.05),对浮游植物密度和总生物量在峰值处的最大抑制率可达75.9%(A组)和83.6%(B组);③框式浮床处理中浮游植物的群落结构比对照处理复杂,A组中浮游植物优势种为隐藻门的卵形隐藻(Cryptomonas ovata)、尖尾蓝隐藻(Chroomonas acuta)和绿藻门的四尾栅藻(Scenedesmus quadricauda)、小空星藻(Coelastrum microporum),B组为隐藻门的尖尾蓝隐藻和裸藻门的梭形裸藻(Euglena acus);④B组试验中,框式浮床处理浮游植物Shannon-Wiener多样性指数显著高于对照处理,生态浮床对浮游植物群落的影响更多体现在提升浮游植物的生物多样性上. 研究表明,浮床系统能高效去除水体N、P,抑制浮游植物的增殖,改变浮游植物的群落结构,并且这些作用受到水体营养水平的影响.      

改性黏土絮凝海洋原甲藻对水体中氮、磷的影响研究

通过对比研究典型有害微藻海洋原甲藻(Prorocentrum micans Ehrenberg)自然消亡(A1组)及改性黏土絮凝(A2组)两种体系,考察两体系中氮、磷等主要水质因子的变化情况.结果表明,改性黏土能有效去除P. micans并影响其后期生长状态,0.4g/L改性黏土添加3.5h后去除率可达60%以上,且藻密度无二次增长.改性黏土絮凝藻华过程中能有效去除水体营养元素, A2组DIP和DIN较A1组分别降低85%和35%.另外,添加改性黏土对水体有机氮、磷影响值得关注,第33d A2组TON和TOP较A1组分别减少约120, 6μmol/L. 改性黏土对有机氮、磷存在一定的埋存保护作用,通过吸附絮凝、螯合等作用使有机氮、磷脱离水体系统,而自然消亡体系中的微藻消亡后将通过分解、矿化等过程快速进入水体参与再循环.该研究系统阐述了改性黏土絮凝P. micans对水体营养环境的影响,以期为现场治理提供理论支持.     

滇池双龙流域不同土地利用方式下土壤侵蚀与土壤养分分异

在滇池双龙流域选取耕地、撂荒地、草地和林地4种土地利用方式,分别取0～40 cm土壤样品,测定样品中的137Cs比活度及w(TN)、w(TP)、w(TOC),同时根据土壤有机质中δ13C(稳定性碳同位素丰度)的剖面分布特征,分析不同土地利用方式对该流域土壤侵蚀程度、土壤养分分异及有机质来源和变化的影响. 结果表明:①耕地、撂荒地、草地和林地土壤的137Cs比活度分别为0.65、0.21、3.92和0.61 Bq/kg,土壤侵蚀模数大小表现为耕地>撂荒地>林地>草地. ②不同土地利用方式下,土壤剖面w(TOC)、w(TN)和w(TP)的平均值差异显著(P<0.001);w(TOC)表现为草地＞林地＞耕地＞撂荒地,w(TN)表现为草地＞耕地＞林地＞撂荒地,w(TP)表现为耕地＞草地＞林地＞撂荒地;各种土地利用方式土壤剖面养分质量分数均随土壤深度增加呈降低趋势. ③耕地、撂荒地、草地和林地土壤的δ13C平均值分别为-22.28‰±1.49‰、-23.29‰±0.24‰、-26.32‰±0.25‰和-25.94‰±0.22‰,推断该区域土壤有机质主要来源于陆生C₃植物. 土壤剖面δ13C的变幅差异反映了土壤有机质分解程度的强弱,δ13C变化规律表现为耕地＞林地＞草地＞撂荒地. ④土壤侵蚀模数越大,w(TOC)和w(TN)越低,草地和林地土壤侵蚀程度较低,土壤养分流失量较小,更有利于土壤质量的改善和流域水环境的保护.      

Indicating landfill stabilization state by using leachate property from Laogang Refuse Landfill

Variation and evolution process of leachate can be applied as a reference for landfill stabilization phase. In this work, leachates with different ages were collected from Laogang Refuse Landfill, and characterized with 14 key parameters. Simultaneously, principal component analysis （PCA） was applied to develop a synthetic parameter-F based on these 14 parameters, and a logarithm equation was simulated for the landfill stabilization process finally. It was predicted that leachates would meet Class I and Class II in standard for pollution control on the landfill site of municipal solid waste （GB 16889-1997） after 32 years and 22 years disposal under the natural attenuation in the humid and warm southern areas of China, respectively. The predication of landfill state would be more accurate and useful according to the synthetic parameter F of leachate from a working landfill.     

N2O emission from a sequencing batch reactor for biological N and P removal from wastewater

Nitrous oxide （N2O） is a greenhouse gas that can be released during biological nitrogen removal from wastewater. N2O emission from a sequencing batch reactor （SBR） for biological nitrogen and phosphorus removal from wastewater was investigated, and the aims were to examine which process, nitrification or denitrification, would contribute more to N2Oemission and to study the effects of heterotrophic activities on N2O emission during nitrification. The results showed that N2O emission was mainly attributed to nitrification rather than to denitrification. N2O emission during denitrification mainly occurred with stored organic carbon as the electron donor. During nitrification, NaO emission was increased with increasing initial ammonium or nitrite concentrations. The ratio of N2O emission to the removed ammonium nitrogen （N2O- N/NH4-N） was 2.5% in the SBR system with high heterotrophic activities, while this ratio was in the range from 0.14% to 1.06% in batch nitrification experiments with limited heterotrophic activities.     

Validation of the UN test method N.5

Many substances react with water in such a way that flammable gases are formed. For transport issues this reaction may possess a considerable hazard especially if the cargo is wetted by rain or by water from other sources. In the UN Recommendations on the Transport of Dangerous Goods these kinds of problems are addressed. The UN test N.5 “Test method for substances which in contact with water emit flammable gases” corresponds to this hazard. Classification according to the test method is done by measurement of the gas evolution rate of the flammable gas by any suitable procedure. At BAM a gravimetric approach is used to measure the gas evolution rate. In this paper we present the evaluation of the apparatus by means of an absolute calibration routine utilizing a reaction where a known amount of gas is produced as well as the evaluation of important parameters influencing the gas evolution rate using different substances. It can be shown that the apparatus is capable of measuring absolute gas volumes as low as 6 mL with an acceptable error of about 17% as determined from the reaction of Mg with demineralized water.     

某水电站库首右岸拉裂变形体形成机理研究

某水电站库首右岸存在一个拉裂变形体,低线施工公路从陡峭拉裂变形体山坡下部通过。低线公路开挖完成后路堑边坡发生局部塌滑,于2003年5月在其上部形成浅层滑坡体(1000多方)。结合拉裂变形体的分析和治理工作,在统计分析大量勘探资料的基础上,提出了该拉裂变形体是边坡在自重应力和构造应力的复合应力场下快速却荷引起岩体的浅表生改造,形成如荷松动岩体,后期在低线公路祠室大爆破开挖施工、下部坡体切脚和基雨的影响下形成浅层滑坡体,并逐步向上扩展的形成机理。     

Short-term influence of nutrient availability on the uptake and translocation of phenanthrene in mangrove seedlings

Abstract

The uptake and distribution of phenanthrene, a typical polycyclic aromatic hydrocarbon, in plant tissues of Aegiceras corniculatum and Avicennia marina and the relationship with nutrient (nitrate, ammonium, and soluble reactive phosphorus) availability were investigated. After 12?h of exposure, enhancements in the concentration of nitrate and soluble reactive phosphorus markedly decreased the residual level of phenanthrene in roots, while the addition of ammonium significantly increased the residual concentration. Due to the similar enzymatic degradation potential between treatment groups, the variation of phenanthrene concentration in mangrove roots may result from the H⁺/phenanthrene cotransport at the root surface that was influenced by nutrient uptake. Moreover, both nitrate and soluble reactive phosphorus amendments significantly increased translocation of phenanthrene from roots to leaves, which likely resulted from the change of hydraulic conductivity in mangrove plants triggered by different nutrient availability.     

The effect of limiting nutrient on metal toxicity to selenastrum capricornutum

Metal toxicity on selenastrum capricornutum were examined by batch culture and chemostat culture system. EC₅₀ values under nutrient‐limited condition and saturated condition were compared. The two EC_5Os differed by a factor of 10.6 for Cd in batch test, and differed by a factor of 6.5 in continuous test. Both batch and continuous test results indicate that inhibition on algal growth is more severe under nutrient‐limited conditions compared to that under near saturation conditions.

Strong correlation, as characterized by the correlation coefficient ρ, were found between the activation level (nutrient requirement) and the tolerance of microorganisms to the toxicant. ρ is equal to 0.9 for the case of Cd in batch test and 0.6 in continuous test. The theory in this study provides generally good estimations to the dose‐response relationship at limiting nutrient conditions. The study indicate that nutrient conditions constitute an important factor in algal toxicity tests.