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1.
Yong Ma Yong‐zhen Peng Xiao‐lian Wang Shu‐ying Wang 《Journal of chemical technology and biotechnology (Oxford, Oxfordshire : 1986)》2005,80(10):1118-1124
The laboratory scale anaerobic–anoxic–aerobic (A2O) process fed with synthetic brewage wastewater was designed to investigate the effects of changing feed C/P ratio on the performance of biological nutrient removal (BNR) processes. In the experiment, the influent chemical oxygen demand (COD) concentration was kept at approximately 300 mg L?1 while the total phosphorus concentration was varied to obtain the desired C/P ratio. Results showed that when the C/P ratio was lower than 32, phosphorus removal efficiency increased as C/P ratio increased linearly, while when the C/P ratio was higher than 32, the P removal efficiency was maintained at 90–98%, and effluent P concentration was lower than 0.5 mg L?1. However, regardless of the C/P ratio, excellent COD removal (90% or higher) and good total nitrogen removal (75–84%) were maintained throughout the experiments. It was also found that very good linear correlation was obtained between COD uptake per unit P released in the anaerobic zone and C/P ratio. In addition, the P content in the wasted activated sludge increased with the decrease in the C/P ratio. Based on the results, it was recommended that the wastewater C/P ratio and its effects be incorporated into BNR design and operational procedures, appropriate C/P ratios were used to achieve the effluent treatment goals. Copyright © 2005 Society of Chemical Industry 相似文献
2.
A.J. MILLER F.J. SCHULTZ A. OSER J.L. HALLMAN S.A. PALUMBO 《Journal of food science》1994,59(4):739-741
Swine carcass microflora were evaluated for selected foodborne pathogens after exposure to reconditioned water during scalding, dehairing, and polishing operations. Reused water had been reconditioned and chlorinated. Rodac plates applied to hams were used to assess carcass microflora. Water samples were enumerated using membrane filtration or spiral plating. Sampling was at mid-week throughout the year. Total aerobic plate counts on hams were unaffected by treating with potable or reconditioned waters. No differences were observed for staphylococci, enterics, fecal streptococci, Listeria monocytogenes, coliforms, and Aeromonas levels. A preevisceration potable water carcass wash reduced the bacterial load, regardless of initial treatment. Bacterial counts on carcasses paralleled those in water. Reuse is an alternative to potable water for initial slaughter operations without diminishing bacteriologic safety. 相似文献
3.
探讨采用先进的A/O(厌氧菌 /好氧菌 )生物脱氮技术对己内酰胺生产废水进行处理的工作机理和工艺设计方法 ,分析了温度、溶解氧、pH值、进水碳氮比等参数对生物脱氮工艺过程的影响 ,并对其关键技术进行了研究 相似文献
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5.
S. Mahimairaja N. S. Bolan M. J. Hedley A. N. Macgregor 《Nutrient Cycling in Agroecosystems》1990,24(3):141-148
Kjeldahl nitrogen (N), total N and forms of inorganic N (ammoniacal (NH4)-N, nitrate (NO3)-N and nitrite (NO2)-N) were measured in a range of animal manures. The manures include fresh samples of poultry manure, sheep manure, horse manure, dairy slurry and pig slurry and composted poultry manure. Kjeldahl N was measured by standard micro-Kjeldahl digestion. For total N measurements, NO3-N and NO2-N were recovered during Kjeldahl digestion by pretreatments with various oxidizing and reducing agents. Inorganic forms of N were measured by extraction with 2M KCl solution.Kjeldahl digestion alone allowed measurement only of organic N and NH4-N. Amongst various modifications to the Kjeldahl, pretreatment with either acidified (H2SO4) Zn-CrK(SO4)2 or acidified (H2SO4) reduced Fe achieved complete recovery of NO3-N. Nitrite N was only recovered by first oxidising the NO
2
-
to NO
3
-
with KMnO4 followed by reduction to NH4-N with acidified (H2SO4) reduced Fe.More than 95% of the total N in fresh animal manure was present as organic N and NH4-N which were recovered by the standard Kjeldahl digestion. In the case of fresh manures there was no difference between the amount of total N measured by the Kjeldahl digestion and its modified methods. However composting of poultry manure or drying of poultry manure, pig slurry and dairy slurry resulted in an increase in NO3-N which was not recovered during Kjeldahl digestion alone. Under these conditions the total N could be measured by pretreating the samples with KMnO4 and reduced Fe prior to Kjeldahl digestion.Drying of animal manures caused a decrease in organic N and NH4-N, especially in poultry, pig and dairy manures. There was a slight increase in NO3-N; but most of the decrease in N content with drying was attributed to the volatilization loss of ammonia (NH3). Amongst various drying methods examined air drying caused maximum loss of N as NH3 whereas freeze drying caused minimum loss of N. This suggests that fresh animal manures can be freeze dried for analysis of N which causes minimum loss of N. 相似文献
6.
仓式静态连续好氧堆肥发酵工艺的水气研究 总被引:2,自引:0,他引:2
采用仓式静态连续好氧堆肥发酵工艺,通过建立水平衡体系,系统地研究了水分对整个发酵工艺的影响,得出了仓式静态连续好氧堆肥发酵具有工艺简便,热交换快,水气蒸发量大等特点;好氧堆肥发酵过程中发酵温度保持在65℃左右,含水量控制在45%~55%有利于有机物降解,垃圾堆肥可在40~50d腐熟;静态连续好氧一次堆肥发酵物料的含水量需控制在35%以下,机械自动分选(类)筛分效率高,筛分率在90%~95%,垃圾减容在50%~60%.二次堆肥发酵物料的含水量需控制在25%~30%,机械除杂(碎石、碎玻璃等)效果好,有机肥中杂质含量低于0.8%.静态好氧二次堆肥发酵可以用垃圾渗沥水补充水分,达到资源循环再利用,可实现污水零排放. 相似文献
7.
采用好氧和厌氧污泥进行污泥的生物吸附实验,研究好氧与厌氧污泥吸附动力学和吸附平衡模型。研究表明:好氧和厌氧污泥的吸附过程中,颗粒内扩散是污泥吸附的主要限速阶段,但它不是唯一的限速因素。好氧和厌氧污泥的假二级反应模型比一级、二级反应模型更能描述污泥的吸附过程。Langmuir和Freundlich的吸附平衡方程都适合描述厌氧和好氧污泥的吸附平衡过程。 相似文献
8.
9.
先通过厌氧消化阶段自然发酵产生的高温杀灭生活垃圾中有害病原微生物;再通过厚层通气发酵阶段黑曲霉的糖化作用和酵母菌生产菌体的增殖,把无机氮转化成酵母菌体有机氮,使产品增加了1.66%的酵母菌体有机氮. 相似文献
10.
白腐菌-厌氧-好氧工艺处理造纸黑液研究 总被引:5,自引:0,他引:5
对白腐菌降解有机物的机理进行了探讨,研究了经驯化后的一株白腐菌处理造纸黑液的最佳工艺路线,白腐菌在最适培养条件(pH值6~7,温度25-29℃)下进行间歇式处理培养5d,出水再续以厌氧 好氧的处理工艺,在不同停留时间取得了相近的处理效果,COD去除率达70%以上。 相似文献