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异养生物

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The test also reveals that the removal of CODCr could not keep in pace with that of ammonia in the process of film formation , while the increasing rate of the aerobic heterotrophic bacteria is higher than that of the autotrophic nitrobacteria in the process of biological film growth.

试验还显示,挂膜过程中,CODCr 和氨氮的去除率的提高不是同步的,生物膜增长过程中,好氧异养菌的增殖速度较快,硝化菌的增殖速度较慢。

And this strain degraded H〓S without lag time. The heterotrophic bacteria's generation period was short and its growth was rapid. The result of experiment indicated when the strain Hm-6 was applying to the packed tower, the startup was more quickly and the control was more convenient than the autotrophic bacterium. Applying to deodorize the H〓S, the better removalability could be got. At the same time, comparing with the system used at home of which the biofilm directly formed with activated sludge, it runs in the neutral condition, has lower corrusivity to the equipment and was liable to handle. And this system didn't need the acclimation to become biofilm, so it can save a rather long acclimation time.

异养菌虽然不以硫化物作为能源物质,但其世代周期短、生长迅速,运行管理比自养菌更为方便,具有周期短,启动迅速等优点,接种了菌株Hm-6泥炭生物填料塔,对低浓度H〓S有较高的去除效果,且没有延迟期,与国内通常采用的直接以活性污泥挂膜的方式相比,应用该菌的脱臭系统在中性条件下运行,对设备的腐蚀性较低、运行过程较易控制,具有很好的应用前景。

The above results are useful for the cultivation of transgenic cyanobacteria in enclosed photobioreactors, and would promote the application of mixotrophic cultivation system in microalgae cultivation. Besides, they are also useful to understand the interrelation between photoautotrophy and heterotrophy in cyanobacteria.

本文的研究结果在实践上可为转基因蓝藻的光生物反应器培养奠定理论和实验基础,同时可促进混合营养培养系统在微藻培养中的应用,在理论上有助于提高人们对于蓝藻光自养和异养代谢的相互作用和蓝藻光合作用及其调控的认识。

During restoration experiment, several functional and structural parameters (number of species, diversity index, percentage of phytomastigophora, community pollution value, heterotrophy index, similarity index between communities) were determined weekly.

在修复实验过程中,定期测定微型生物群落的各种结构和功能参数(种类数,多样性指数,植鞭毛虫百分比,群落污染值,异养性指数,群落结构的相似性指数),通过它们的变动机制和规律,再现了修复过程中微型生物群落的演替过程。

The journal covers research on viruses, prokaryotes and eukaryotes - both planktonic and benthic, autotrophic and heterotrophic - in marine, limnetic and brackish habitats.

该期刊涵盖了对病毒、原核生物和真核生物的研究,包括浮游生物和底栖生物,自养生物和异养生物,海洋生物、湖沼生物及半咸水生物。

As nonmotile heterotrophs, fungi must eventually be able to find new sources of nutrients.

作为不会移动的异养生物,真菌最终能够发现营养新资源的。

A few heterotrophic organisms are phototrophic (i.e. show photoheterotrophism).

少数几种异养生物是光合营养的。

Because energy transformation cannot be 100% efficient, heterotrophsmust have less energy,and must therefore be rater than the plants they feed on.

因为能量转换不可能100%的有效,因此异养生物的能量较少,必然比它们所吃的植物更少。

Because energy transformation cannot be 100% efficient, heterotrophs must have less energy,and must therefore be rater than the plants they feed on.

因为能量转换不可能100%的有效,因此异养生物的能量较少,必然比它们所吃的植物更少。

According to the above study result, the diversity of microorganisms population in the SUFR system is complex and the bio-community formed in the SUFR system is stable. The close relations between abundance of bacteria and nutrients were found. The correlation between heterotrophic bacteria and COD was 0.949. The correlation between organic phosphate bacteria and TP was 0.815. The correlation between nitrosobacteria and NH3-N was 0.909. The correlation between disnitrifier bacteria and TN was 0.653. These inneglectable great factors effecting on phosphorus-uptake and phosphorus-release of phosphorus accumulating organisms are the influent COD、the concentration of DO、the sludge retention time、the temperature. The diversity of organic phosphate bacteria population in the SUFR reactor was complex and there is no phosphate bacteria taking the absolute superiority in quantity. The near-native pure culture method powerfully complement the traditional pure culture technique and enrich culture technique. The sludgy bioactivity is very good in whole SUFR reactor. By the quality of being biochemistry, the anaerobic phase is higher than anoxic phase and the anoxic phase is higher than aerobic phase of SUFR.

通过以上试验内容研究发现,SUFR 系统中的微型动物种群较多,微生物生态系统稳定;系统中微生物的数量与营养盐的含量密切相关,其中总异养菌与COD的相关系数r 为0.949,有机磷细菌与TP 的相关系数r 为0.815,亚硝化菌与NH4+-N的相关系数r 为0.909,反硝化菌的数量和TN 的相关系数r 为0.653;污水生物除磷工艺中进水COD 的浓度、DO 浓度、泥龄的长短、温度都是影响聚磷菌释磷及吸磷效果的不可忽视的因素;SUFR 系统中的磷细菌呈现种群多样化的趋势,没有占绝对优势数量的磷细菌;微孔滤膜近自然培养法是对传统纯培养技术和富集培养技术的有力补充;整个SUFR 反应器系统中污泥的生物活性很好,就可生化性来讲,厌氧反应器大于缺氧反应器大于好氧反应器;按照动力学方程式求出的细胞生长动力学特征值和SUFR 脱氮除磷系统工艺的实测值结果基本吻合。

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