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    • 1. 发明授权
    • Self-adjusting fluid surface skimmer and fluid treatment system using same
    • 自调节流体表面撇渣器和流体处理系统使用相同
    • US06821415B2
    • 2004-11-23
    • US10075076
    • 2002-02-13
    • Matthew L. Sharb
    • Matthew L. Sharb
    • C02F312
    • B01D19/02B01D21/003B01D21/0042B01D21/02B01D21/2405B01D21/2433C02F3/12C02F2303/12Y02W10/15
    • A self-adjusting fluid surface skimmer and a wastewater treatment system incorporating the same are provided. In one embodiment, the skimmer includes an intake passage and an outlet passage. The intake passage comprises first and second passageways connected by a flexible coupling. A collar is positioned around the first passageway near an intake opening. At least one buoyant member is attached to the collar and facilitates self-adjustment of the skimmer. A gas inlet is disposed in the outlet passage and allows for the movement of gas through the outlet passage, which creates a suction effect in the intake passage. The wastewater treatment system comprises an aeration tank disposed in a settling tank such that a clearance is created between the two tanks. A skimmer according to the present invention is disposed within the clearance. The skimmer enables further removal of solids from treated fluid within the settling tank prior to leaving the treatment system.
    • 提供了一种自调节流体表面撇渣器和包括其的废水处理系统。 在一个实施例中,撇渣器包括进气通道和出口通道。 进气通道包括通过柔性联轴器连接的第一和第二通道。 衣领位于靠近进气口的第一通道周围。 至少一个浮力构件附接到套环上并且促进撇渣器的自调节。 气体入口设置在出口通道中,允许气体通过出口通道移动,这在进气通道中产生吸力。 废水处理系统包括设置在沉淀池中的曝气池,使得在两个罐之间产生间隙。 根据本发明的撇渣器设置在间隙内。 在离开处理系统之前,撇渣器能够进一步从沉淀池内的处理过的流体中除去固体。
    • 3. 发明授权
    • Method for controlling aeration systems of biological tanks treating waste water
    • 控制处理废水的生物罐曝气系统的方法
    • US06290850B1
    • 2001-09-18
    • US09509799
    • 2000-06-02
    • Patrice ChatellierPhilippe Caulet
    • Patrice ChatellierPhilippe Caulet
    • C02F312
    • G05D21/02C02F3/006C02F2209/22C02F2209/40Y02W10/15
    • Method of monitoring the efficiency of the aeration systems of biological basins of a wastewater treatment plant, characterized in that it consists in: i) measuring the throughput (Qt) of the plant and the rate (Qr) of recirculation of the mixed liquor from the clarifier to the aeration basin; and ii) measuring the concentration of dissolved oxygen in the aeration basin so as: a) to establish, during an aeration period, the material balance between oxygen supplied, oxygen consumed and oxygen discharged with the effluent; b) to establish, during a non-aeration period, the material balance between oxygen consumed and oxygen discharged with the effluent; c) to determine the amount of oxygen consumed by the biomass based on the two material balances established above; and d) to determine, from the data obtained at a), b) and c) , the value of the transfer coefficient &agr;kLa under the conditions of the measurement.
    • 监测污水处理厂生物盆地曝气系统效率的方法,其特征在于:i)测量植物的通过量(Qt)和混合液体的再循环速率(Qr) 澄清池到曝气池; 和ii)测量曝气池中溶解氧的浓度,以便:a)在曝气期间建立氧气供应量,消耗的氧气与排出的氧气之间的物质平衡; b) 曝气期间,消耗的氧气与排出的氧气之间的物质平衡; c)根据上述两种物料平衡确定生物质消耗的氧气量; andd)根据a),b)和c)中获得的数据确定在测量条件下的传递系数alphakLa的值。
    • 5. 发明授权
    • Apparatus and process for biological wastewater purification
    • 生物废水净化装置及工艺
    • US06620323B2
    • 2003-09-16
    • US09745066
    • 2000-12-21
    • Stefan HotherGerhard ProbstKlaus RocznikBernd Striegel
    • Stefan HotherGerhard ProbstKlaus RocznikBernd Striegel
    • C02F312
    • C02F3/1257B01D21/003B01D21/0045B01D21/01B01D21/06B01D21/2466B01D21/2488C02F3/12Y02W10/15
    • The present invention relates to an apparatus and a process for biological wastewater purification. According to the invention an activation tank (10) is provided in which, with feed of a catalyst, wastewater constituents are degraded by degradation means (11), for example microorganisms, suspended in the wastewater. In the activation tank (10) is disposed at least one lamellae pack (50) in or on which the degradation means (11) suspended in the wastewater are separated out by sedimentation to fall as thickened sedimentation means sludge (11′) to the bottom region (15) of the activation tank (10). In the said bottom region (15) of the activation tank (10) is provided forced recirculation (20, 22) of the degradation means, which takes up the thickened degradation means sludge (11′) and recirculates it as suspended degradation means (11) back to the activation tank (10).
    • 本发明涉及一种用于生物废水净化的装置和方法。 根据本发明,提供了一种活化罐(10),其中在催化剂的进料中,废水组分由悬浮在废水中的降解装置(11),例如微生物降解。 在活化罐(10)中设置至少一个薄片包装(50),其中悬浮在废水中的降解装置(11)通过沉降分离出来,由于增稠的沉降意味着污泥(11')到底部 活性罐(10)的区域(15)。 在所述活化槽(10)的所述底部区域(15)中设置有降解装置的强制再循环(20,22),所述降解装置占据所述增稠的降解装置污泥(11')并将其作为悬浮的降解装置(11 )回到活化罐(10)。
    • 7. 发明授权
    • Method for purifying carbon-containing pollution and denitrifying waste water in oxygenic medium
    • 含氧污染净化方法和含氧介质中的废水脱氮方法
    • US06254778B1
    • 2001-07-03
    • US09254173
    • 1999-03-02
    • Pavel ChudobaClaude GrimaudRoger Pujol
    • Pavel ChudobaClaude GrimaudRoger Pujol
    • C02F312
    • C02F3/06C02F3/006C02F3/12C02F3/30C02F3/302C02F2209/04C02F2209/14C02F2209/15Y02W10/15
    • The invention is a biological process for purifying waste water in order to produce an effluent with a low content of carbon and of oxygenated nitrogen compounds. The process includes an initial step of mixing the waste water in a biological reactor with activated sludge to denitrify the resulting mixture. Then, air is introduced into the mixture to form an anoxic sludge thereby directly oxidizing carbon present in the anoxic sludge and removing carbon therefrom, simultaneous with the denitrification. The anoxic sludge is clarified to separate it from a denitrified intermediate effluent. The clarified anoxic sludge is recycled to the biological reactor. Then, intermediate effluent is nitrified to form a nitrified liquor and a portion of the nitrified liquor is recycled into the anoxic sludge that is present in the biological reactor, thereby subjecting the anoxic sludge to oxygen present in nitrified compounds and consequently further removing carbon from the anoxic sludge, simultaneous with the denitrification. The rate of removal of carbon is controlled as a function of the flow rate/pollution characteristics of the anoxic sludge while a redox potential of the anoxic sludge is continuously measured. A nitrate concentration of the intermediate effluent is continuously measured. There is an adjustment of an amount of air introduced into the anoxic sludge in accordance with the measured redox potential and measured nitrate concentration. A recycling flow rate of the nitrified liquor is adjusted in accordance with the measured redox potential and measured nitrate concentration. The remaining nitrified liquor is the final effluent.
    • 本发明是用于净化废水以生产低碳含量和含氧氮化合物的流出物的生物过程。 该方法包括将生物反应器中的废水与活性污泥混合以使得到的混合物脱氮的初始步骤。 然后,将空气引入混合物中以形成缺氧污泥,从而直接氧化存在于缺氧污泥中的碳,并与脱氮同时除去碳。 澄清缺氧污泥以将其与反硝化中间体流出物分离。 澄清的缺氧污泥被再循环到生物反应器中。 然后,将中间体流出物硝化以形成硝化液,并将一部分硝化液循环到存在于生物反应器中的缺氧污泥中,从而使缺氧污泥对存在于硝化化合物中的氧进行再次除去, 缺氧污泥,同时脱氮。 作为缺氧污泥的流量/污染特性,连续测定缺氧污泥的氧化还原电位,控制碳的除去速度。 连续测量中间体流出物的硝酸盐浓度。 根据测量的氧化还原电位和测量的硝酸盐浓度,调节引入到缺氧污泥中的空气量。 根据测得的氧化还原电位和测量的硝酸盐浓度调节硝化液的再循环流量。 剩余的硝化液是最后的废水。
    • 9. 发明授权
    • Wastewater treatment process
    • US06585895B2
    • 2003-07-01
    • US09767478
    • 2001-01-23
    • Stephen A. SmithHoward E. C. Brown
    • Stephen A. SmithHoward E. C. Brown
    • C02F312
    • C02F3/1221C02F1/66C02F3/342Y02W10/15
    • There is provided a process for treating industrial wastewater that substantially eliminates the generation of excess solids in the system requiring mechanical removal. The wastewater undergoes an equalization step wherein hydraulic flow is smoothed and the pH of the wastewater is adjusted to near neutral pH conditions. The equalized wastewater is then transferred to aeration tanks where the organic process wastes are absorbed, metabolized, or otherwise biodegraded by the microorganisms in the mixed liquor in the aeration tanks. After the aeration step, the wastewater is separated by gravity in a clarifying step to separate the wastewater into a liquid phase and a semi-solid phase. The clarified liquid phase is withdrawn from the clarifier and discharged, while the semi-solid phase is transferred either directly back to the aeration/biological treatment step, as recycle-activated sludge, or into a bioreactor as waste-activated sludge. In the bioreactor the semi-solid phase is subjected to active aeration. The aerated waste-activated sludge is then batch-recycled to the equalization tank discharging to the aeration step where it is mixed into newly introduced untreated wastewater and undergoes a new cycle of biological treatment. As a result of the indirect batch-recycling of bioreactor waste-activated sludge into the mixed liquor (biomass containing waste sludge) under aeration, which is also receiving recycle-activated sludge and enzymes, the excess solids generated in this process virtually eliminated.
    • 10. 发明授权
    • Activated sludge wastewater treatment system and method
    • 活性污泥废水处理系统及方法
    • US06488854B2
    • 2002-12-03
    • US09947982
    • 2001-09-06
    • Kevin P. O'LearyThomas H. ProbstJenchie WangDavid A. WilsonHenry J. Probst
    • Kevin P. O'LearyThomas H. ProbstJenchie WangDavid A. WilsonHenry J. Probst
    • C02F312
    • C02F3/1221C02F3/006C02F3/12C02F3/286C02F3/30C02F2209/06Y02W10/15
    • A improved activated sludge system and method for treating wastewater containing contaminants is disclosed which offers a broad array of advantages over conventional activated sludge wastewater treatment systems, including smaller size, higher rates of operation, higher oxygen transfer efficiency, lower operating costs, and a substantially decreased level of excess sludge production. The improved activated sludge waste treatment system of the present invention has two processing tanks rather than the several tanks that are commonly found in activated sludge systems for treatment and sludge management equalizations, including anaerobic processes. The first processing tank is a contact tank which hosts a reaction which functions not merely to digest the maximum amount of contaminants, but instead to bind contaminants to the microorganisms through absorption, adsorption, precipitation, or digestion so that they can then be removed from the liquid in a solid/liquid separator. The activated sludge removed by the solid/liquid separator is then supplied to a digester tank containing a high concentration of activated sludge, where virtually complete digestion is achieved to minimize the volume of solids remaining. Activated sludge is provided from the digester tank to the contact tank to facilitate the reaction in the contact tank.
    • 公开了一种改进的活性污泥系统和用于处理含有污染物的废水的方法,其提供了比常规活性污泥废水处理系统广泛的优点,包括较小的尺寸,较高的操作速率,更高的氧气转移效率,更低的运行成本, 污泥产量过剩水平下降。 本发明的改进的活性污泥废物处理系统具有两个处理槽,而不是在活性污泥系统中通常存在的用于处理和污泥管理平衡的几个罐,包括厌氧处理。 第一个处理罐是接触罐,其承载反应,其功能不仅仅是消化最大量的污染物,而是通过吸收,吸附,沉淀或消化将污染物与微生物结合,从而可以将它们从 液体在固/液分离器中。 然后将由固体/液体分离器除去的活性污泥供应到含有高浓度活性污泥的蒸煮罐,其中实际上完全消化以使剩余的固体的体积最小化。 活性污泥从蒸煮罐提供到接触罐,以便于接触罐中的反应。