会员体验
专利管家(专利管理)
工作空间(专利管理)
风险监控(情报监控)
数据分析(专利分析)
侵权分析(诉讼无效)
联系我们
交流群
官方交流:
QQ群: 891211   
微信请扫码    >>>
现在联系顾问~
热词
    • 1. 发明专利
    • Anaerobic treatment system and method
    • 厌氧处理系统和方法
    • JP2014184382A
    • 2014-10-02
    • JP2013060363
    • 2013-03-22
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社National Institute For Environmental Studies独立行政法人国立環境研究所
    • FUJIMOTO NORIYUKIINABA HIDEKITAMATSUBO KAZUAKI
    • C02F3/28C02F1/70
    • C02F3/286C02F3/2846C02F3/2893C02F2203/002Y02E50/343
    • PROBLEM TO BE SOLVED: To suitably perform anaerobic treatment by suppressing rising of the oxidation reduction potential of organic wastewater in an anaerobic treatment tank.SOLUTION: An anaerobic treatment system has a configuration where a part of biogas generated by anaerobic treatment in an anaerobic treatment tank 12 is returned to a balancing tank 9 and an acid production tank 11 located upstream of the anaerobic treatment tank 12. Consequently, hydrogen sulfide contained in the biogas is dissolved into organic wastewater to increase the concentration of sulfide ions in the organic wastewater, whereby the oxidation reduction potential of the organic wastewater can be maintained at a low level. As a result, even when the concentration of organic substances in the organic wastewater is low and when the oxygen consumption is not sufficient due to insufficient decomposition of the organic substances by microorganisms in low-temperature anaerobic treatment or the like, rising of the oxidation reduction potential of the organic wastewater can be suppressed to suitably perform anaerobic treatment.
    • 要解决的问题:通过抑制厌氧处理槽中的有机废水的氧化还原电位的上升来适当地进行厌氧处理。解决方案:厌氧处理系统具有这样的结构,其中在厌氧处理槽中通过厌氧处理产生的一部分沼气 12返回到位于厌氧处理槽12上游的平衡罐9和酸生产槽11.因此,包含在沼气中的硫化氢溶解到有机废水中以增加有机废水中硫化物离子的浓度,由此 有机废水的氧化还原电位可维持在较低水平。 结果,即使当有机废水中的有机物质的浓度低时,由于低温厌氧处理等中的微生物的有机物质的分解不足,氧消耗不足时,氧化还原的上升 可以抑制有机废水的潜力以适当地进行厌氧处理。
    • 2. 发明专利
    • Treatment method and treatment apparatus for organic waste water
    • 有机废水处理方法及处理装置
    • JP2005185967A
    • 2005-07-14
    • JP2003430983
    • 2003-12-25
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社
    • CHIKU HARUYUKIINABA HIDEKI
    • C02F3/28C02F11/00
    • Y02W10/12
    • PROBLEM TO BE SOLVED: To provide a treatment method capable of highly treating even organic waste water containing sulfate ion or sulfite ion. SOLUTION: The treatment method includes a 1st step for carrying out an acid formation treatment of the organic waste water containing sulfate ion and/or sulfite ion and for reducing the sulfate ion and/or sulfite ion to form sulfide, a 2nd step for adding an iron salt based inorganic flocculant into the organic waste water obtained by the 1st step and containing the sulfide to flocculate the sulfide to be separated from the organic water water and a 3rd step for anaerobically treating the organic waste water which is obtained in the 2nd step and from which the sulfide is separated. The methane fermentation of organic components in the organic waste water is smoothly carried out in the anaerobic treatment because the sulfate ion and the sulfite ion are removed from the organic waste water before the anaerobic treatment. COPYRIGHT: (C)2005,JPO&NCIPI
    • 要解决的问题:提供能够高效处理含有硫酸根离子或亚硫酸根离子的有机废水的处理方法。 解决方案:处理方法包括用于对含有硫酸根离子和/或亚硫酸根离子的有机废水进行酸形成处理并用于还原硫酸根离子和/或亚硫酸根离子以形成硫化物的第一步骤,第二步骤 用于将铁盐无机絮凝剂加入到通过第一步获得的有机废水中并含有硫化物以使待分离的硫化物从有机水中絮凝,并且在第三步骤中对在有机废水中获得的有机废水进行无氧处理 第二步,硫化物从中分离。 有机废水中的有机成分的甲烷发酵在厌氧处理中顺利进行,因为在厌氧处理之前将硫酸根离子和亚硫酸根离子从有机废水中除去。 版权所有(C)2005,JPO&NCIPI
    • 4. 发明专利
    • 活性汚泥処理方法
    • 主动污泥处理方法
    • JP2014205122A
    • 2014-10-30
    • JP2013085034
    • 2013-04-15
    • 住友重機械工業株式会社Sumitomo Heavy Ind Ltd
    • SUEHIRO BUNICHIINABA HIDEKI
    • C02F3/12
    • Y02W10/15
    • 【課題】シグナル物質による微生物の活性の調節をより効率的に行う。【解決手段】活性汚泥処理装置100における通常の曝気処理中の曝気槽内の活性汚泥の濃度よりも濃度が高い状態にある活性汚泥に対してシグナル物質を添加する構成とすることで、曝気処理中に曝気槽2内に分散されている活性汚泥にシグナル物質を添加する場合と比較して、より濃縮された状態で活性汚泥に対してシグナル物質を添加するので、シグナル物質が分散する前に活性汚泥内の微生物に対して好適に作用することができ、その結果、シグナル物質による微生物の活性の調節をより効率的に行うことができる。【選択図】図1
    • 要解决的问题:通过信号物质有效调节微生物的活性。解决方案:一种活性污泥处理方法包括在普通曝气中将浓度高于曝气池中活性污泥浓度的活性污泥加入信号物质 在活性污泥处理装置100中进行处理。由于将信号物质添加到更浓缩的活性污泥中,与曝气处理时分散在曝气池2中的活性污泥中添加信号物质的情况相比, 信号物质可以在其分散之前对活性污泥中的微生物有期望地起作用,从而通过信号物质更有效地调节微生物的活性。
    • 5. 发明专利
    • Method for predicting abundance of specific microorganism in sludge at some time point in future
    • 在未来几个时间点预测泥沙中特定微生物污染的方法
    • JP2010022317A
    • 2010-02-04
    • JP2008189935
    • 2008-07-23
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社
    • INABA HIDEKIHASHIMOTO YOHEI
    • C12Q1/68C02F3/12C02F3/34C12N15/09C12Q1/06
    • Y02W10/15
    • PROBLEM TO BE SOLVED: To provide a method whereby, when biological discharged water treatment equipment is newly started up, a suitable acclimatization period and an optimal load of the biological discharged water treatment equipment are predicted and the start-up of the biological discharged water treatment equipment is smoothly promoted.
      SOLUTION: The method is for predicting the abundance of a specific microorganism in sludge at a some time point in future in biological discharged water treatment equipment for decomposing a processing object substance in discharged water. The method includes a measurement step for measuring the abundance of the specific microorganism in sludge at plural time points by using a real time PCR method, a calculation step for calculating a specific growth rate of the specific microorganism based on the abundance of the specific microorganism at plural time points, and a prediction step for predicting the abundance of the specific microorganism at a some time point in future based on the specific growth rate.
      COPYRIGHT: (C)2010,JPO&INPIT
    • 要解决的问题:为了提供一种新生物排泄水处理设备的初始化时,可以预测生物排泄水处理设备的合适的适应期和最佳负荷,并且启动生物排泄水处理设备 排水处理设备顺利推进。 解决方案:该方法用于预测未来某个时间点污泥中特定微生物的丰度,用于生物排放水处理设备中用于分解出水中的加工对象物质。 该方法包括通过使用实时PCR方法来测定多个时间点的污泥中的特定微生物的丰度的测量步骤,用于基于特定微生物的丰度计算特定微生物的比生长速率的计算步骤 多个时间点,以及用于在将来的某个时间点基于特定生长速率预测特定微生物丰度的预测步骤。 版权所有(C)2010,JPO&INPIT
    • 6. 发明专利
    • Granular sludge producing method
    • 颗粒泥浆生产方法
    • JP2007253106A
    • 2007-10-04
    • JP2006083136
    • 2006-03-24
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社
    • INABA HIDEKI
    • C02F3/10C02F3/00C02F3/12
    • Y02W10/15
    • PROBLEM TO BE SOLVED: To provide a granular sludge producing method by which granular sludge can be more quickly produced. SOLUTION: The granular sludge producing method has an agglomerate sludge producing process of producing agglomerate sludge G2 having two or more pieces of flocculated sludge G1 by agglomerating the flocculated sludge G1 and a granular sludge producing process of producing granular sludge G3 by propagating microorganisms in the flocculated sludge G1 contained in the agglomerate sludge G2. In the agglomerate sludge producing process, the flocculated sludge G1 is agglomerated by utilizing viscous polysaccharide. Since the viscous polysaccharide is utilized in the agglomerate sludge producing process in this way, time of forming the agglomerate sludge G2 from the flocculated sludge G1 is shortened. Consequently the granular sludge G3 can be more quickly formed. COPYRIGHT: (C)2008,JPO&INPIT
    • 要解决的问题:提供一种可以更快速地生产颗粒污泥的颗粒污泥的生产方法。 解决方案:颗粒状污泥生产方法具有附聚污泥生产方法,其通过使絮凝污泥G1凝聚来生产具有两个或更多个絮凝污泥G1的附聚污泥G2,以及通过传播微生物产生颗粒污泥G3的颗粒污泥生产方法 在凝聚污泥G2中所含的絮凝污泥G1中。 在附聚污泥生产过程中,絮凝的污泥G1通过利用粘性多糖凝聚。 由于粘附多糖以这种方式用于附聚污泥生产过程中,所以缩短了从絮凝淤泥G1形成附聚污泥G2的时间。 因此,粒状污泥G3可以更快地形成。 版权所有(C)2008,JPO&INPIT
    • 8. 发明专利
    • Methane fermentation method and methane fermentation device
    • 甲烷发酵方法和甲烷发酵装置
    • JP2006026536A
    • 2006-02-02
    • JP2004209095
    • 2004-07-15
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社
    • INABA HIDEKI
    • C02F3/28
    • Y02E50/343
    • PROBLEM TO BE SOLVED: To provide a methane fermentation method and a methane fermentation device which can carry out methane fermentation in good condition and in stable condition. SOLUTION: The decomposition reaction of substances releasing a large amount of hydrogen during the decomposition reaction is carried out stepwise sequentially in pretreatment reaction tanks 1a, 1b connected to the former stage of a methane reaction tank 2 in order. The total hydrogen released by the decomposition reaction is separately released in a plurality of the pretreatment reaction tanks 1a, 1b, and hydrogen accumulation in liquid of each reaction tank is reduced to lower the partial pressure of hydrogen, which facilitates the decomposition reaction from propionic acid to acetic acid. COPYRIGHT: (C)2006,JPO&NCIPI
    • 要解决的问题:提供甲烷发酵方法和能够在良好状态和稳定状态下进行甲烷发酵的甲烷发酵装置。 解决方案:在分解反应期间释放大量氢的物质的分解反应依次在与甲烷反应槽2的前一级连接的预处理反应槽1a,1b中依次进行。 通过分解反应释放的总氢分解释放在多个预处理反应槽1a,1b中,并且减少每个反应罐的液体中的氢积聚,以降低氢的分压,这有利于从丙酸分解反应 到乙酸。 版权所有(C)2006,JPO&NCIPI
    • 10. 发明专利
    • Method and program for estimating microorganism activity, biological treatment method using the same, and computer readable recording medium
    • 用于评估微生物活动的方法和程序,使用该微生物活性的生物处理方法和计算机可读记录介质
    • JP2003080281A
    • 2003-03-18
    • JP2001280276
    • 2001-09-14
    • Sumitomo Heavy Ind Ltd住友重機械工業株式会社
    • INABA HIDEKINAKAJIMA SHINOBU
    • C12N1/00C02F3/00C02F3/28C02F3/34G06F17/13
    • Y02W10/12
    • PROBLEM TO BE SOLVED: To provide a method and program for estimating microorganism activity which can be easily operated and managed and can efficiently perform a biological treatment and to provide a biological treatment method using the same, and a computer readable recording medium recorded with this program. SOLUTION: In the method of estimating the microorganism activity state in a biological treatment vessel 2 of a complete mixing type, a substrate concentration Sin is measured, the substrate concentration S in treated wastewater is further measured, (dS/dt)c is calculated from (dS/dt)c=(F/V)(Sin -S) (V is the volume of the biological treatment vessel 2, (dS/dt)c is a microorganism activity parameter) in a stationary state in accordance with Sin and S, S' is calculated from S'=[(F/V).Sin +(dS/dt)c-A.exp(F.t/V)]/(F/V) (A is an integration constant) in a non-stationary state, (dS/dt)c is charged until this S' coincides with the actually measured value S of the substrate concentration, and (dS/dt)c is calculated when S coincides with the value.
    • 要解决的问题:提供一种用于估计微生物活性的方法和程序,其可以容易地操作和管理,并且可以有效地进行生物处理,并提供使用该方法和程序的生物处理方法,以及记录有该程序的计算机可读记录介质 。 解决方案:在完全混合型的生物处理容器2中估计微生物活性状态的方法中,测量底物浓度Sin,进一步测量处理废水中的底物浓度S,(dS / dt)c由 (dS / dt)c =(F / V)(Sin -S)(V是生物处理容器2的体积,(dS / dt)c是微生物活性参数) S,S'是从非易失性存储器中的S'= [(F / V).Sin +(dS / dt)cA.exp(Ft / V)] /(F / V)(A是积分常数) 静电状态(dS / dt)c被充电直到该S'与衬底浓度的实际测量值S一致,并且当S与该值一致时,计算(dS / dt)c。