湖北九宫山甜槠群落结构与优势种的空间分布格局研究

通过对湖北九宫山国家级自然保护区甜槠群落建立的1ha固定森林样地进行植物群落调查,分析了样地内木本植物物种组成、区系成分、种群径级结构和空间分布格局,结果表明:(1)样地内木本植物(DBH≥1 cm)共有132种,隶属于42科78属,其中,杜鹃花科、壳斗科、樟科、蔷薇科、冬青科等是优势科,短柄袍、鹿角杜鹃、青冈、长叶石栎、甜槠等是优势种.(2)样地内植物科、属的分布类型均以泛热带分布类型为主,分别为30.95％和20.51％.(3)样地内所有木本植物个体的径级结构均呈倒"J"型,幼龄个体数量大,森林群落更新状况良好.(4)样地内木本植物个体的空间分布格局以聚集分布为主,部分优势物种在小尺度上呈聚集分布,而在较大尺度上则为随机分布.     

Research progress and hot spots of hydrothermal liquefaction for bio-oil production based on bibliometric analysis

Environmental Science and Pollution Research - Hydrothermal liquefaction (HTL) of biomass used HTL reaction under high temperature and pressure to produce bio-oil. This technology is considered as...     

原子荧光法测定水中汞的原子化条件研究

分别采用热原子化原子荧光法(热汞法)和冷原子化原子荧光法(冷汞法)测定水中汞,比较了两种方法的检出限、线性相关系数、准确度和精密度的差异。冷汞法和热汞法的检出限分别为0.003和0.01μg/L,标准曲线相关系数分别为0.999 9和0.999 7,加标回收率范围分别为102%~106%和106%~113%。结果表明,冷汞法比热汞法具有更低的检出限,灵敏度和准确度也略优于热汞法。对于冷汞法,提高负高压有利于提高方法的灵敏度、准确度,并具有更低的方法检出限。     

Mitigating Impact of Devils Lake Flooding on the Sheyenne River Sulfate Concentration

Devils Lake is a terminal lake located in northeast North Dakota. Because of its glacial origin and accumulated salts from evaporation, the lake has a high concentration of sulfate compared to the surrounding water bodies. From 1993 to 2011, Devils Lake water levels rose by ~10 m, which flooded surrounding communities and increased the chance of an overspill to the Sheyenne River. To control the flooding, the State of North Dakota constructed two outlets to pump the lake water to the river. However, the pumped water has raised concerns about of water quality degradation and potential flooding risk of the Sheyenne River. To investigate these perceived impacts, a Soil and Water Assessment Tool (SWAT) model was developed for the Sheyenne River and it was linked to a coupled SWAT and CE‐QUAL‐W2 model that was developed for Devils Lake in a previous study. While the current outlet schedule has attempted to maintain the total river discharge within the confines of a two‐year flood (36 m³/s), our simulation from 2012 to 2018 revealed that the diversion increased the Sheyenne River sulfate concentration from an average of 125 to >750 mg/L. Furthermore, a conceptual optimization model was developed with a goal of better preserving the water quality of the Sheyenne River while effectively mitigating the flooding of Devils Lake. The optimal solution provides a “win–win” outlet management that maintains the efficiency of the outlets while reducing the Sheyenne River sulfate concentration to ≤600 mg/L.     

利用毒代动力学模型研究氟虫腈在夹杂带丝蚓体内的手性选择性积累过程

农药的生物积累直接影响其毒性,但是手性农药在生物体内的选择性积累过程仍不明确.本文在恒定环境水浓度的条件下,开展手性农药氟虫腈的外消旋体及其对映体在底栖无脊椎动物夹杂带丝蚓体内的生物积累实验.在96 h和72 h的吸收和消除实验过程中,测定生物体内的氟虫腈的外消旋体和对映体浓度随时间的变化情况,构建毒代动力学模型,获取吸收和消除速率常数.结果表明夹杂带丝蚓对R-氟虫腈的生物浓缩因子(1981 L·kg~(-1)脂肪)比对S-氟虫腈(1748 L·kg~(-1)脂肪)更大.R-氟虫腈和S-氟虫腈的吸收速率常数相当,分别为311±11 L·kg~(-1)脂肪·h~(-1)和313±13 L·kg~(-1)脂肪·h~(-1),而R-氟虫腈的消除速率常数小于S-氟虫腈,分别为0.157±0.006 h~(-1)和0.179±0.008 h~(-1),因此相对较慢的消除是导致R-氟虫腈在夹杂带丝蚓体内更高生物积累的主要原因.研究说明毒代动力学参数可有效阐释手性外源物质在生物体内选择性积累的差异.     

电化学开关表面活性剂对芘的可逆增溶作用

表面活性剂增强修复技术(SER)是目前行之有效的有机污染土壤修复技术,但SER技术存在表面活性剂与污染物分离困难、易导致二次污染、成本高等问题.基于此,提出采用具有电化学开关特性的表面活性剂(N,N-二甲基二茂铁甲基十二烷基溴化铵,Fc12)代替SER技术中的常规表面活性剂,发展基于开关表面活性剂的可逆增强修复技术(RSER).选取芘作为目标物,研究了Fc12在氧化和还原态对芘的增溶作用以及常见环境因素,如pH和温度对Fc12可逆增溶的影响.结果表明,相对于氧化态Fc12,还原态Fc12在其临界胶束浓度(CMC)以上时对芘表现出显著的增溶作用,且增溶能力随表面活性剂浓度增大而增强.温度对Fc12的增溶作用影响显著,例如,还原态Fc12在浓度为3 mmol·L~(-1)、25℃条件下时,芘的表观溶解度为0.779 mg·L~(-1),当温度增加到40℃时,芘的表观溶解度为0.971 mg·L~(-1),其表观溶解度增加了24.6%;但氧化态条件下,芘的表观溶解度仅增加了6.5%;芘的解吸率(芘在还原和氧化态Fc12的表观溶解度差值与还原态Fc12增溶芘的比值)由63.67%增加到71.27%.pH也显著影响Fc12的增溶,当pH值在6—10范围变化时,还原态Fc12的增溶作用呈现先增加后减小的趋势,且在pH 9附近增溶能力最强,而pH 8时芘的解吸果最好.     

土壤中挥发性芳香烃的顶空前处理方法研究

本方法针对土壤中挥发性芳香烃顶空前处理条件进行了研究,优化了顶空密封垫的选择、顶空平衡温度、加热平衡时间、进样时间和顶空瓶压力等顶空前处理条件,测定条件科学、准确,完全能够满足土壤中挥发性芳香烃监测分析的灵敏度和准确度相关的技术要求。该方法精密度为1.7%~9.8%,准确度为34.3%~83.7%,检出限为2.0~4.2μg/kg。为制订土壤中挥发性芳香烃监测分析方法提供了技术支持。     

基于压力响应关系法的湖泊营养物基准制定

湖泊富营养化与氮、磷及有机物含量过高密切相关,建立数字型营养物基准能够防止富营养化对水体指定用途造成影响.太湖流域是我国华东地区经济腹地,近年来流域内湖泊水质每况愈下,对其基准研究可为湖泊治理提供依据.详细介绍了压力响应关系法制定湖泊营养物基准的步骤,并将此方法运用到太湖流域营养物基准制定研究中.为满足大多数水体指定用途,研究中将该流域湖泊基本功能确定为娱乐、永生生物栖息地及饮用水,以此构建流域概念模型.选择压力变量为总氮(TN)、总磷(TP)和有机物,响应变量为叶绿素a(chl-a).用非参数分析法和线性回归法分别建立压力-响应模型,通过2种方法相互验证得到TN、TP和CODMn基准分别为0.593、0.067和4.092 mg/L.     

16S rDNA克隆文库解析AO-MBR系统中细菌种群多样性

采用分子生物学手段16S rDNA克隆文库方法对缺氧/好氧膜生物反应器(AO-MBR)的好氧池与缺氧池中细菌进行了多样性研究.实验结果表明,好氧池污泥样品的克隆文库包括9个类群,其中变形菌(Proteobacteria)和拟杆菌(Bacteroidetes)在文库中所占比例最大,分别为37.04％和14.81％;其次是酸杆菌(Acidobacteria)、未培养菌(uncultured bacterium)、绿菌(Chlorobi)和未培养的绿弯菌(uncultured Chloroflexi bacterium)、浮霉状菌(Planctomycetes),分别为11.11％、11.11％、7.41％、7.41％和5.56％;硝化螺旋菌(Nitrospirae)和裸藻门(Euglenozoa)所占比例相对较小,均为1.85％.缺氧池样品克隆文库包括10个类群,其中变形菌(Proteobacteria)、拟杆菌(Bacteroidetes)和未培养菌(uncultured bacterium)在文库中所占比例最大,分别为27.91％、13.95％和12.79％;其次是浮霉状菌(Planctomycetes)、酸杆菌(Acidobacteria)和绿弯菌(Chloroflexi),在文库中所占比例分别为9.3％、9.3％和9.3％;硝化螺旋菌(Nitrospirae)、裸藻门(Euglenozoa)、芽单胞菌(Gemmatimonadetes)和放线菌(Actinobacteria)所占比例相对较少,分别为6.98％、8.14％、1.16％和1.16％.两池细菌的主要类群相似,但菌属及比例有所差异,变形菌是系统中的主要脱氮菌属.     

The ageing effect on the bioaccessibility and fractionation of arsenic in soils from China

Ingestion of contaminated soil has been recognized as an important exposure pathway of arsenic for humans, especially for children through outdoor hand-to-mouth activities. An improved sequential extraction procedure was employed in an attempt to reveal the relationship between bioaccessibility and fractionation of As in five soils from China. Arsenic bioaccessibility in acidic ( approximately pH 4.5) soils reached approximately stable levels after a sharp decline within one week of ageing. In contrast, As bioaccessibility in higher pH (>6.0) soils was found to be significantly higher and took two weeks of ageing to reach stable levels. The artificially added As was more labile than indigenous As. The main proportions of added As were found in the specifically sorbed and amorphous and poorly-crystalline hydrous Fe/Al oxide-bound fractions. Correlation analysis shows that the non-specifically and specifically sorbed As are likely to constitute the main proportion of bioaccessible soil As. The soil content of amorphous and crystalline Fe/Al oxides and soil pH appear to be the key factors controlling, not only the time needed to reach a steady state, but also the magnitude of the bioaccessibility of As added to the soils.