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cod相关的网络例句
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LWhen the unacclimated UASB reactor, acclimated UASB reactor and anerobic filter were shockcdy by the combined load, the largest increase of the effluent COD under combined load shocking was higher than that of the sum of chloroform (or 2,4-dinitrophenol, noted DNP) and COD load shocking independently.

2多负荷冲击(COD+CF+DNP+ALK)按照正交试验来设计,反应器UASB-RⅠ在多负荷冲击时,影响出水VFA的因素的主次顺序为CF>COD>DNP>ALK;影响出水DNP的因素的主次顺序依次为DNP>CF>COD>ALK;影响VGP和%CH_4的因素的主次顺序分别为CF>DNP>COD>ALK、CF>DNP>COD>ALK。

Cod ( Gadus morhua L.) PRELIMINARY STUDY OF DIET OF PACIFIC COD, Gadus macroce Phalus Tilesius

的两个地理种群:苏格兰西海岸和波罗的海鲱、大西洋鳕 Gadus morhua L。

Norway sea water is cold and clean and rich of halobios. Norway cod lives in deep ocean in the Arctic Circle. The Norway cod nutrition is better for the excellent natural environment.

挪威海水温度低,海洋生物丰富,无污染,鳕鱼生长在北极圈深海中,得天独厚的自然环境使这种鱼的营养价值高出一筹。

The results show that after adding RBW 0.5-2.5% bentonite, the highest removal of COD and Kjeldahl Nitrogen was 32% and 24%; after adding RWB 1~5% lime, the highest removal of COD and Kjeldahl Nitrogen was 34% and 40%.

结果表明按土水比添加0.5%~2.5%的膨润土处理后,废水中的COD和凯氏氮的最高去除率分别为32%和24%;添加1%~5%的生石灰处理后,废水中的COD和凯氏氮的最高去除率分别为34%和40%。

Either of two edible marine fishes,Microgadus tom cod of North American Atlantic waters or M.proximus of northern Pacific waters,related to and resembling the cod .

小鳕,近鳕以下两种可食性海鱼中的任意一种:产于北美洲大西洋海域的小鳕和产于太平洋北部水域的近鳕,它与鳕鱼有亲戚关系且外形似鳕

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。

It was revealed that the balanced DO concentration appeared soon after the reaction stage starting,and DO level rose quickly in large range when COD was degraded to its nondegradation concentration under that condition,no matter that change the aeration rate or the MLSS concentration in large range,or change the initial COD concentration gradually or suddenly in the various experimental conditions.

结果表明,无论使曝气量或初始污泥浓度大幅度变化,还是逐渐或突然改变初始有机物浓度等各种试验条件,都会在反应阶段开始不久出现所谓平衡DO浓度现象;当有机物达到其难降解浓度时DO浓度迅速地大幅度升高。

Anaerobic biological deodorization system was able to work steadily even when COD concentration of influents reached 10000mg/L, olfactometry measurement was fitted 5-grade standard and volumetric loading rates were 10.58Kg. COD/; In the two combined UASB systems, Hydraulic Retention Time of the first UASB was 28h, olfactometry measurement of effluents was fitted 3-grade standard; and when HRT of the second UASB was 67h, olfactometry measurement was below 2-grade.

COD〓,厌氧反应器可稳定运行,并具有优良的除臭性能;对两级串联的UASB系统,一级水力停留时间为28h时,出水臭气强度可达3级;二级水力停留时间为67h时,二级出水臭气强度可在2级以下。

The RE of TP, COD and turbidity except NH4+-N in the aeration process by adding AS and PAM for enhanced chemical phosphorus removal increased by 7.3~59.2%, 5.0~20.3% and 10.9~34.7%, respectively. Given enough dissolved oxygen, the nitrification was not affected by adding AS and PAM in the dosage range of the study. The RE of TP, COD and turbidity by postpose coagulation were better than by simultaneous coagulation, however, coagulation and sedimentation equipments were needed in postpose coagulation process. Therefore simultaneous coagulation was more suitable for transformation of AB process for chemically enhanced phosphorus removal.

曝气过程中投加AS和PAM复配化学强化除磷,总磷、COD、浊度去除率分别提高了7.3~59.2%、5.0~20.3%、10.9~34.7%,但不能提高氨氮的去除率;在溶解氧足够时,本研究投加量范围的AS和PAM的加入对硝化作用无影响;后置混凝对TP、COD、浊度的去除效果优于同步混凝,但需增加混凝沉淀设备,因此同步混凝更适合于于AB工艺的化学强化除磷改造。

The average removal efficiency of TP and COD was 28.76% and 8% after cloth media filter without coagulation, and TP removal was influenced by the influent water quality. However, precoagulation with coagulants of ferric chloride, PAFC, PAC, the average removal efficiency of TP was 63.58%, 60.13% and 66.94% respectively, and no influence of TP removal can be found by the influent water quality. The average removal efficiency of COD was of 17.7%,26.3% and 27.7%,SS was 70.7%,64.3% and 49.1%.

当不投加混凝剂时,滤布滤池对TP和COD的平均去除率为28.76%和8%,其中TP的去除效果受进水水质影响较大;当投加氯化铁、聚合氯化铝铁与聚合氯化铝强化滤布滤池时,滤布滤池对TP的平均去除率分别为63.58%、60.13%和66.94%,TP去除效果受进水水质影响较小;对SS的平均去除率分别为70.7%、64.3%和49.1%;对COD平均去除率分别为17.7%、26.3%和27.7%。

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