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    • 1. 发明授权
    • Waste water purification process with batchwise supply of waste water to
the activated sludge tank
    • 废水净化过程,向活性污泥池分批供应废水
    • US5019266A
    • 1991-05-28
    • US174386
    • 1988-03-28
    • Carl-Johannes SoederErich ZandersThomas RaphaelHeiner KeusenJoost Groeneweg
    • Carl-Johannes SoederErich ZandersThomas RaphaelHeiner KeusenJoost Groeneweg
    • C02F3/00C02F3/30
    • C02F3/302C02F3/006C02F3/301C02F2209/15C02F2209/22C02F2209/44Y02W10/15Y10S210/903
    • Aerobic purification of waste water with intermittent batchwise supply of waste water to the activated sludge tank from which the treated waste water drains continuously is disclosed, in which the nitrate content in the waste water is simultaneously reduced by throttling the aeration of the activated sludge tank, starting with the admission of the waste water to the tank, to values equivalent to less than or equal to 0.5 mg/l dissolved oxygen. In particular, aeration may be off until such time as the nitrate content in the tank has dropped below 5 mg/l, in particular below 1 mg/l. In the case of urban waste waters a cycle time of about 1 hour is expediently employed under these circumstances and the aeration is shut off for about 5 minutes, starting from the rapid admission of the waste water charge. Preferably, inlet charges are less than or equal to 30%, in particular between about 5% and 20%, of the tank capacity. In this procedure, nitrate present is degraded in the phase involving oxygen throttling, while in the subsequent phase (over longer times) ammonium fed in with the waste water supplied is converted into nitrate, provision being made for a sufficient population of nitrifying bacteria in the tank.
    • 公开了对经过处理的废水连续排出的活性污泥槽间歇地间歇地供给废水的废水的有氧净化,其中通过节流活性污泥槽的通风同时降低废水中的硝酸盐含量, 从废水进入罐开始,达到相当于0.5mg / l溶解氧的值。 特别是,曝气可能会停止,直到罐中的硝酸盐含量降至5 mg / l以下,特别是低于1 mg / l。 在城市废水的情况下,在这种情况下方便地使用约1小时的循环时间,并且从快速进入废水装置开始,通风关闭约5分钟。 优选地,入口电荷小于或等于罐容量的30%,特别是约5%至20%。 在该方法中,存在的硝酸盐在涉及氧气节流的阶段中降解,而在随后的阶段(更长时间)中,供给的废水中的铵转化为硝酸盐,为了足够的硝化细菌群体提供 坦克。
    • 3. 发明授权
    • Method of treating agricultural wastes
    • 农业废弃物处理方法
    • US4432869A
    • 1984-02-21
    • US413485
    • 1982-08-31
    • Joost GroenewegManfred Schluter
    • Joost GroenewegManfred Schluter
    • C02F3/12C02F3/32C02F3/34
    • C02F3/121C02F3/32C02F3/34Y02W10/15Y02W10/37
    • Purification of liquid agricultural wastes, such as, in particular, liquidanure, by means of an algae/bacteria mixture culture and a subsequent rotifer culture in a separate stage. The pH-value of the algae/bacteria mixture culture is controlled, especially by the waste water charging thereof, in such a way that a multiplication of rotifers in this stage is inhibited or precluded. The algae/bacteria mixture culture preferably occurs in shallow open air ponds for a period of time which depends upon the temperature and can amount to three to six days at a mean temperature of approximately 18.degree. C. The hold time of the algae/bacteria suspension which is in the rotifer container and is adjusted to a pH of 6 to 8 can range from two to four days at a temperature of approximately 20.degree. C. A waste water treatment plant or system for the foregoing includes at least one algae/bacteria mixture culture reservior and at least one rotifer reactor.
    • 通过藻类/细菌混合物培养物和随后的轮状培养在单独的阶段中纯化液体农业废物,特别是液体粪便。 控制藻类/细菌混合培养物的pH值,特别是通过对其进行废水的充填,可以抑制或排除这一阶段的轮虫的繁殖。 藻类/细菌混合培养物优选在浅的露天池塘中发生一段时间,这取决于温度,并且可以在约18℃的平均温度下进行三至六天。藻类/细菌悬浮液的保持时间 在约20℃的温度下,其在轮虫容器中并被调节至6至8的pH可以在2至4天的范围内。上述废水处理设备或系统包括至少一种藻类/细菌混合物 培养池和至少一个轮虫反应器。
    • 4. 发明授权
    • Method of treating liquid agricultural wastes
    • 液体农业废物处理方法
    • US4348285A
    • 1982-09-07
    • US239118
    • 1981-02-27
    • Joost GroenewegManfred Schluter
    • Joost GroenewegManfred Schluter
    • C02F3/12C02F3/32C02F3/34
    • C02F3/121C02F3/32C02F3/34Y02W10/15Y02W10/37
    • Purification of liquid agricultural wastes, such as, in particular, liquidanure, by means of an algae/bacteria mixture culture and a subsequent rotifer culture in a separate stage. The pH-value of the algae/bacteria mixture culture is controlled, especially by the waste water charging thereof, in such a way that a multiplication of rotifers in this stage is inhibited or precluded. The algae/bacteria mixture culture preferably occurs in shallow open air ponds for a period of time which depends upon the temperature and can amount to three to six days at a mean temperature of approximately 18.degree. C. The hold time of the algae/bacteria suspension which is in the rotifer container and is adjusted to a pH of 6 to 8 can range from two to four days at a temperature of approximately 20.degree. C. A waste water treatment plant or system for the foregoing includes at least one algae/bacteria mixture culture reservoir and at least one rotifer reactor.
    • 通过藻类/细菌混合物培养物和随后的轮状培养在单独的阶段中纯化液体农业废物,特别是液体粪便。 控制藻类/细菌混合培养物的pH值,特别是通过对其进行废水的充填,可以抑制或排除这一阶段的轮虫的繁殖。 藻类/细菌混合培养物优选在浅的露天池塘中发生一段时间,这取决于温度,并且可以在约18℃的平均温度下进行三至六天。藻类/细菌悬浮液的保持时间 在约20℃的温度下,其在轮虫容器中并被调节至6至8的pH可以在2至4天的范围内。上述废水处理设备或系统包括至少一种藻类/细菌混合物 培养池和至少一个轮虫反应器。