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zoogloea相关的网络例句

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与 zoogloea 相关的网络例句 [注:此内容来源于网络,仅供参考]

Since the acetic acid bacteria are known to be aerobic, sample A without the oxygen consequently produced no vinegar and no zoogloea.

他发现康普茶生长在正常条件下10天之后只有约0.1g/L醋酸但葡萄糖酸和乳酸多达15倍。

Mainly increasing alkalinity and sludge loading in the reactor for microbial condition where zoogloea grew easily, we added Javel water and ferrous sulfate on side, and sludge bulking was well under control.

试验以增加反应器内的碱度和污泥负荷来提供适应菌胶团生长的微生物环境为主,同时投加次氯酸钠杀菌剂和硫酸亚铁絮凝剂来辅助控制污泥膨胀。

Significant loss of GEMs was not observed but strong growth activities, formation of biofilm and zoogloea on the surface of immobile particles were observed via scanning electron microscope. The mechanical stability of the particles remained unchanged after nearly two-month operation.

在整个反应过程中,没有出现大量工程菌流失的现象,同时在固定化颗粒的表面以及浅层均观察到了大量工程菌菌体,固定化颗粒的表面还出现了生物膜和菌胶团,反应结束时,颗粒形态完好,强度满足本工艺条件下长期使用的需求。

Observed the influences of changing organic load on main microbe, the results showed that high load can cause the nematode mass rearing, made the sludge abnormal and the effluent quality bad. Branched zoogloea possesses stronger tolerance for water quality and shock loading, so did not change.

四,人为的改变有机负荷,观察其对于主体微生物的影响,结果表明高负荷容易引起线虫的大量繁殖,使得污泥发生异常,出水水质差,而主体微生物枝状菌胶团对冲击负荷的耐受力较强,并未发生明显改变。

Poly β hydroxybutyric acid; Zoogloea ; op timized optimal culture medium ; fermentation conditions

聚β-羟基丁酸;动胶菌;优化培养基;发酵条件

Deterioration of SVIs is observed after increasing sludge load to 0.57kgBOD/kgMLSS·d which is related to the excessive growth of Zoogloea colonies.

当活性污泥中含聚磷菌时,系统长期在有机负荷为0.2和0.26kgBOD/kgMLSS·d条件下运行,污泥沉降性能良好。

HP3 identified as Zoogloea sp. is an effectively strain. Under the optimal degradation condition and ABAS concentration of 200~1200mg/L, the ABAS degradation followed negative exponential model. With the ABAS concentration increasing, the ABAS degradation was greatly regressed. Temperature was the most important factor influencing ABAS degradation. The functions of specific growth rate and temperature, degradation rate of ABAS and temperature were constructed respectively.

菌株HP3是一高效降解溴胺酸的菌株,经鉴定为动胶菌属;在最佳降解条件下,溴胺酸浓度在200~1200mg/L时,其降解遵从负指数方程,溴胺酸浓度大于1200mg/L时,降解受到显著的抑制;温度是影响菌体生长及降解溴胺酸的最显著因素,建立了菌体比生长速率-温度和溴胺酸降解率-温度曲线方程。

The recorded genera are as follows: Pseudomonas, Flavobacterium, Alcaligens, Achromobacler, Zoogloea, Bacillus, Micrococcus and Arthrobacter.

经鉴定,所获菌株归纳为八个属,其中数量最多的优势属是假单胞杆菌属和黄杆菌属。

The possible pathway of ABAS degraded by Zoogloea HP3 was that ABAS was first cleaved to produce o-phthalic acid and products. The former was further degraded and the composites of the latter were 2-amino-3-hydroxyl-5bromobenzenic sulfonic sodium and 2, 3-dihydroxyl-5-bromobenzenic sulfonic sodium.

动胶菌HP3作用下溴胺酸可能的降解途径为蒽醌环开裂生成中间产物邻苯二甲酸,邻苯二甲酸被进一步降解;溴胺酸降解后的最终产物为2-氨基-3-羟基-5-溴苯磺酸钠和2,3-二羟基-5-溴苯磺酸钠。

ABAS could be decolored by extracellular composite enzymes secreted by Zoogloea HP3. The degradation place of o-pathalic acid was in-cell. Compared with the degradation of o-pathalic acid, the decoloring of ABAS controlled the degradation of ABAS.

动胶菌HP3分泌的胞外组成酶可使溴胺酸脱色,溴胺酸降解中间产物邻苯二甲酸的降解场所在胞内;与邻苯二甲酸的降解相比,溴胺酸的脱色是反应的控制步骤。

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