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    • 2. 发明专利
    • Method for treating boron-containing water
    • 用于处理含硼水的方法
    • JP2003080269A
    • 2003-03-18
    • JP2001271428
    • 2001-09-07
    • Kurita Water Ind LtdTohoku Electric Power Co Inc東北電力株式会社栗田工業株式会社
    • HAYASAKA TAKAOYAMAURA TSUGUAKISATO TAKESHIETO YOSHIHIROASADA HIROYUKI
    • C02F1/52C02F1/42C02F1/58
    • PROBLEM TO BE SOLVED: To provide a method for treating boron-containing water by which the amount of chemicals used and the regeneration frequency of an ion exchange resin are reduced and boron can be efficiently removed by flocculation precipitation and/or ion exchange.
      SOLUTION: (1) In the method for treating boron-containing water by flocculation precipitation, the concentration of boron in the boron-containing water is automatically analyzed and the amount of a flocculant added is automatically controlled. (2) When the boron-containing water is treated by an ion exchange method, the concentration of boron is automatically analyzed and time appropriate to the regeneration of an ion exchange resin is automatically controlled. (3) When the boron-containing water is treated by the ion exchange method after treatment by flocculation precipitation, the concentration of boron is automatically analyzed and the amount of a flocculant added is automatically controlled.
      COPYRIGHT: (C)2003,JPO
    • 要解决的问题:提供一种处理含硼水的方法,通过该方法可以减少使用的化学品的使用量和离子交换树脂的再生频率,并且可以通过絮凝沉淀和/或离子交换有效地除去硼。 解决方案:(1)在通过絮凝沉淀处理含硼水的方法中,自动分析含硼水中硼的浓度,并自动控制添加的絮凝剂的量。 (2)当通过离子交换法处理含硼水时,自动分析硼的浓度,自动控制适合离子交换树脂再生的时间。 (3)当通过絮凝沉淀处理后,通过离子交换法处理含硼水时,自动分析硼的浓度,并自动控制添加的絮凝剂的量。
    • 6. 发明专利
    • MEMBRANE SEPARATOR
    • JPH0929073A
    • 1997-02-04
    • JP18706895
    • 1995-07-24
    • TOHOKU ELECTRIC POWER COKURITA WATER IND LTD
    • ISHIYAMA KAZUHIROSASAKI YUSATO TAKESHIMATSUTANI NAOKIHIROTA MORIYUKI
    • B01D65/02B01D65/08
    • PROBLEM TO BE SOLVED: To prolong the life of a membrane by preventing the recontamination of the membrane after backward washing. SOLUTION: In a membrane separator taking out the transmitted water of a membrane module 1 through a backward washing pressure tank 2, a backward washing passage 13B having a valve V1 opened only at a time of backward washing and a transmitted water taking-out passage 13A having a valve Vs permitting only the flow in a forward direction from the membrane module 1 to the backward washing pressure tank 2 and a constant flow valve Vf making this flow constant are provided. In a backward washing process, the transmitted water in the tank 2 is allowed to flow backward to the transmitted water chamber 1b of the membrane module 1 through the backward washing passage 13B. The transmitted water is always taken out of the membrane module 1 through the transmitted water taking-out passage 13A having the constant flow valve Vf. Since the flow rate of transmitted water becomes constant even immediately after backward washing, the recontamination of a membrane by the flow of a large quantity of transmitted water after backward washing is prevented.
    • 7. 发明专利
    • TREATMENT OF WASTE WATER CONTAINING SULFURIC ACID
    • JPH10137770A
    • 1998-05-26
    • JP30473796
    • 1996-11-15
    • TOHOKU ELECTRIC POWER COKURITA WATER IND LTD
    • FUJITA HIROYUKINIHEI MIKIOCHIKASAWA KIYOHITOTAKADOI TADASHISATO TAKESHI
    • C02F1/44C02F1/58
    • PROBLEM TO BE SOLVED: To prevent reduction in membrane flux due to clogging, breakage, etc., of membranes, to stabilize the treatment and to improve efficiency of the treatment by adding a calcium compound to waste water contg. sulfuric acid in two stages, i.e., in a first stage and a second stage respectively to adjust pH of the waste water to specified values in the first and second stages respectively, subjecting insoluble matter thus formed in the resulting water to membrane separation to obtain permeant water and discharging the permeant water to the outside of the treatment system as treated water. SOLUTION: In the system of this treatment, waste water contg. sulfuric acid is introduced into a first reaction vessel 1 fitted with a pH meter IA and thereafter, a calcium compound such as Ca(OH)2 , or the like is added to the waste water to adjust the pH to 4 to 6, or preferably, about 4.5 to 5.5. Then, this waste water is further introduced into a second reaction vessel 2 fitted with a pH meter 2A and similarly, a calcium compound is added to the waste water to adjust the pH to 6.5 to 8. The resulting water is treated with a circulation vessel 3 and a membrane module 5, to obtain membrane permeant water. The permeant water is transferred to a permeant water tank 6 for backwashing to discharge the permeant water from the tank 6 to the outside of the system as treated water. By performing the addition of a calcium compound to waste water contg. sulfuric acid and the adjustment of pH of the waste water in two stages, the dissolution amounts of scale-forming components can sufficiently be reduced and also, deposition of coarse particles can be prevented from occurring. Thus, trouble due to scale formation, membrane breakage, etc., can be prevented from being caused.
    • 8. 发明专利
    • TREATMENT METHOD FOR MANGANESE-CONTAINING WASTEWATER
    • JPH0929267A
    • 1997-02-04
    • JP18706595
    • 1995-07-24
    • TOHOKU ELECTRIC POWER COKURITA WATER IND LTD
    • ISHIYAMA KAZUHIROSASAKI YUTAKADOI TADASHICHIKASAWA KIYOHITOMITA MASAICHIROSATO TAKESHI
    • C02F1/64
    • PROBLEM TO BE SOLVED: To stably and efficiently treat manganese-containing wastewater, e.g. flue gas desulfurization wastewater, by making manganese insoluble by adding a permanganate to the manganese-containing wastewater and then insolubilizing the remaining permanganate by adding a sulfur-containing compound and successively separating insoluble substances by solid-liquid separation. SOLUTION: Manganese-containing wastewater, e.g. flue gas wastewater, is led to an adjustment tank 1, pH of the wastewater is adjusted to be 8.0-9.5 by adding an alkali such as NaOH and, at the same time, air aeration is carried out by an air bubbling pipe 13. Next, the wastewater flowing out of the adjustment tank 1 is led to a first reaction tank 2 and fluorine is converted into an insoluble substance by adding a permanganate, e.g. KMnO4 , or an aluminum compound, an alkali, etc., and adjusting pH to about 6.0-7.5. After that, the resultant wastewater flowing out of the first reaction tank 2 is led to a second reaction tank 3 and the permanganate is converted into an insoluble substance by adding a sulfur-containing compound. The obtained wastewater flowing out of the second reaction tank 3 is then led to a membrane separation apparatus 5 through a circulation tank 4 and a pump P and the insoluble substances are separated and removed.