牡丹江流域水质变化趋势及水环境污染特征研究

通过对牡丹江近10年水质监测、评价及变化趋势研究,采用单项污染指数评价法、环境功能区达标评价法,评价牡丹江丰水期、平水期、枯水期水质现状,给出超标项目与超标倍数,计算污染分担率、污染负荷比,绘制主要污染物各断面浓度变化图,总结牡丹江污染特点和水质变化趋势,得出牡丹江水环境污染特征,为环境管理提供科学依据。     

利用酒糟生产饲料蛋白的菌种选育

为了提高酒糟蛋白质的含量和粗纤维的降解,本研究选菌种３０株,以白酒糟为原料筛选出优质饲料蛋白菌株８５０２,８５０３和８５０５三株。用微生物液体发酵法,经研究发现,以８５０３和８５０５组成的多菌发酵体系,使酒糟初始蛋白含量由２３．０％。     

5% Bestox 乳剂在棉田内的残留动态试验

5％Bestox乳剂为氯氰菊酯类型的杀虫剂,通用名Alphamethrin,中文暂用名腈二氯苯醚菊酯。化学名称:(±)L-氰基-3苯氧苄基(±)-顺-反-2.2-二甲基-3-(2,2-二氯乙烯基)环丙烷-1-羧酸酯。分子式 C_(22)H_(19)Cl_2NO_3,分子量416.31,结构式     

落实科学发展观 加速绿色景区创建

旅游业是社会经济的重要组成部分,但其发展过程中出现了严重的资源破坏、环境污染问题,甚至影响到它进一步发展。绿色景区创建是改变旅游业粗放经营现状、解决旅游环境问题、构建和谐社会的需要。本文阐述了绿色景区的基本内涵与创建意义,指出绿色景区创建的基本任务、方法程序和核心内容以及绿色景区创建的支撑条件与技术保障措施,为绿色景区创建提供基本思路,对旅游业持续发展具有积极意义。     

天然河流纵向离散系数的最优化计算方法及其应用

提出了计算天然河流纵向离散系数的最优化方法，并用此法对岷江蕨溪段的试验数据进行处理，计算出了该段河流的纵向离散系数。     

新化矿区煤矸石中微量元素赋存形态及浸出特征

利用BCR连续提取法和浸泡实验,对贵州省新化煤矿区不同风化程度的煤矸石中微量元素As、Cd、V、Zn、Co、Cr、Cu、Ni、Pb的赋存形态及浸出浓度进行研究。赋存形态研究结果表明:在煤矸石中As和Cd元素主要以酸溶态、可还原态和可氧化态形式赋存,而其他微量元素V、Zn、Co、Cr、Cu、Ni、Pb主要以残渣态形式赋存;除了V元素的赋存形态含量百分比不受煤矸石风化程度影响外,其它微量元素的赋存形态的含量百分比均会受到煤矸石风化程度的影响。煤矸石的浸出实验表明:浸泡时间是影响煤矸石中微量元素释放的一个重要因素;在浸泡过程中,大部分微量元素在浸泡前期的浸出浓度受煤矸石风化程度的影响,Zn和Cu元素则是在整个浸泡过程的浸出浓度均受到煤矸石风化程度的影响;不同粒径大小的煤矸石在浸泡过程中,除微量元素As和Co的浸出浓度不受煤矸石粒径大小的影响,其他微量元素在浸泡前期和中期的浸出浓度均与煤矸石的粒径大小呈反比。     

UASB反应器快速启动的试验研究

在中温条件下投加颗粒活性炭可加快ＵＡＳＢ反应器颗粒化进程。通过对比试验,表明投加和不投加活性炭的反应吕处理石化石废水污泥颗粒化时间分别为３９ｄ和６２ｄ。投加活性炭反应器的颗粒污泥粒径也较大。最大ＣＯＤ去除率在８６％以上。并且投加活性炭反应器的有机负荷为不投加的２倍,运行效果更稳定。     

山东烟台金斗山金矿非金属矿物成因矿物学研究

对产于烟台金斗山金矿内的贯通性非金属矿物石英及碳酸盐类的化学成分、晶体习性、流体包裹体和天然热发光特征做了研究 ,结果表明 ,矿床的主成矿阶段的环境介质为酸性偏中性 ,富矿和贫矿石英的热发光曲线均为双峰型 ,但峰点温度、总积分强度有显著差异。碳酸盐类矿物的总体演化趋势为从富镁铁向富钙方向演化 ,碳酸盐热发光曲线的峰型和积分强度是判别成矿期和非成矿期碳酸盐的可信参数。     

Toxicity and subcellular distribution of cadmium in wheat as affected by dissolved organic acids

We aim to investigate the effects of humic acid (HA) and citric acid (CA) on the toxicity and subcellular distribution of Cd in wheat. Results show that the toxicity and uptake of Cd decreased with increasing HA. The EC₅₀ values of Cd increased from 3.36 μmol/L to 4.96 and 7.33 μmol/L at 50 and 250 mg/L HA, respectively, but decreased to 1.39 μmol/L in the presence of CA based on free ion activity model (FIAM). HA decreased the relative subcellular distribution of Cd in the heat-denatured proteins (decreased from 54% to 33%) but increased Cd in the heat-stable proteins in root (from 25% to 50%) at 7.61 μmol/L {Cd²⁺} (free Cd activity), which resulted in decreasing Cd toxicity. However, CA increased Cd toxicity due to the increased internalization of Cd although the relative subcellular distributions of Cd exhibited a decrease in the heat-denatured proteins and increase in the granule fraction compared to the control at high-level Cd. The FIAM could not predict the toxicity of Cd in the presence of organic acids. Alternatively, the internal Cd accumulation and subcellular Cd concentration were better to describe the toxicity of Cd to wheat.     

Effects of productivity on biodiversity in forest ecosystems across the United States and China

In the global campaign against biodiversity loss in forest ecosystems, land managers need to know the status of forest biodiversity, but practical guidelines for conserving biodiversity in forest management are lacking. A major obstacle is the incomplete understanding of the relationship between site primary productivity and plant diversity, due to insufficient ecosystem‐wide data, especially for taxonomically and structurally diverse forest ecosystems. We investigated the effects of site productivity (the site's inherent capacity to grow timber) on tree species richness across 19 types of forest ecosystems in North America and China through 3 ground‐sourced forest inventory data sets (U.S. Forest Inventory and Analysis, Cooperative Alaska Forest Inventory, and Chinese Forest Management Planning Inventory). All forest types conformed to a consistent and highly significant (P < 0.001) hump‐shaped unimodal relationship, of which the generalized coefficients of determination averaged 20.5% over all the forest types. That is, tree species richness first increased as productivity increased at a progressively slower rate, and, after reaching a maximum, richness started to decline. Our consistent findings suggest that forests of high productivity would sustain few species because they consist mostly of flat homogeneous areas lacking an environmental gradient along which a diversity of species with different habitats can coexist. The consistency of the productivity–biodiversity relationship among the 3 data sets we examined makes it possible to quantify the expected tree species richness that a forest stand is capable of sustaining, and a comparison between the actual species richness and the sustainable values can be useful in prioritizing conservation efforts.