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    • 2. 发明申请
    • METHODS OF CATIONIC POLYMER DETECTION
    • 阳离子聚合物检测方法
    • WO2012083492A1
    • 2012-06-28
    • PCT/CN2010/002112
    • 2010-12-21
    • GENERAL ELECTRIC COMPANYZHANG, GuixiWANG, SijingXU, HongTANG, Xiaofeng
    • ZHANG, GuixiWANG, SijingXU, Hong
    • G01N31/22
    • G01N21/49
    • A method of detecting cationic polymers involves: obtaining a target water sample containing a cationic polymer; adding a polymer dispersant solution and a phosphate solution to the target water sample, the polymer dispersant solution is comprised of a polymer dispersant with calcium and magnesium hardness and the phosphate solution is comprised of a phosphate; standing the target water sample; and measuring the turbidity of the target water sample; comparing the turbidity of said target water sample with a calibration curve of the turbidity of samples containing known concentrations of cationic polymers to determine the concentration of cationic polymers in said target water sample.
    • 检测阳离子聚合物的方法包括:获得含有阳离子聚合物的目标水样品; 将聚合物分散剂溶液和磷酸盐溶液加入到目标水样品中,聚合物分散剂溶液由具有钙和镁硬度的聚合物分散剂组成,磷酸盐溶液由磷酸盐组成; 站在目标水样上; 并测量目标水样品的浊度; 将所述目标水样品的浊度与含有已知浓度的阳离子聚合物的样品的浊度的校准曲线进行比较,以确定所述目标水样品中阳离子聚合物的浓度。
    • 3. 发明申请
    • METHODS FOR BIOLOGICAL PURIFICATION OF WASTE OR WASTEWATER
    • 废水或废水生物净化方法
    • WO2009117209A1
    • 2009-09-24
    • PCT/US2009/034623
    • 2009-02-20
    • GENERAL ELECTRIC COMPANYWANG, Sijing
    • WANG, Sijing
    • C02F3/34
    • B09C1/10B09B3/00B09C1/002C02F1/444C02F3/30C02F3/348C02F2101/105C02F2101/16C02F2101/30
    • A method for purifying a waste environment including treating a portion of the waste environment to inactivate or diminish native microoganisms, adding augmenting microorganisms to the treated waste environment, simultaneously growing and acclimating a microbiological culture and discharging the microbiological culture to the waste environment. The method provides improved biological purification of waste and in-situ bio augmentation. A method of purifying wastewater comprising treating a portion of the wastewater to inactivate or diminish native microorganisms, adding augmenting microoganisms to the furhter treated portion of wastewater, simultaneously growing and acclimating a microbiological culture, discharging the microbiological culture to the wastewater, proliferating the microbiological culture in the waste environment to break down organic and inorganic matter in the wastewater and separating purified wastewater from the biomass.
    • 一种用于净化废弃环境的方法,包括处理废弃环境的一部分以灭活或减少天然微生物,向经处理的废弃环境中加入增加的微生物,同时生长和适应微生物培养物并将微生物培养物排放到废物环境中。 该方法提供改进的废物生物净化和原位生物增殖。 一种净化废水的方法,包括处理一部分废水以灭活或减少天然微生物,向废水处理的部分添加增加的微生物,同时生长和适应微生物培养,将微生物培养物排放到废水中,增殖微生物培养物 在废物环境中分解废水中的有机和无机物质,并将净化废水与生物质分离。
    • 4. 发明申请
    • METHOD OF BIOGAS PRODUCTION ENHANCEMENT USING CATIONIC POLYMER
    • 使用阳离子聚合物生物生产增强的方法
    • WO2013033865A1
    • 2013-03-14
    • PCT/CN2011/001529
    • 2011-09-09
    • GENERAL ELECTRIC COMPANYLI, JieCHEN, JingLUO, JingWANG, SijingXIAO, WeiminYIN, QinghuaZHANG, Guixi
    • LI, JieCHEN, JingLUO, JingWANG, SijingXIAO, WeiminYIN, QinghuaZHANG, Guixi
    • C02F3/28
    • C02F3/28C02F1/56C02F2303/06Y02E50/343
    • A method of biogas production enhancement for an anaerobic digestion process is provided. The method of biogas production enhancement uses a cationic polymer to improve the efficiency of converting organic waste into biogas, such as methane containing gas. The cationic polymers typically used are a copolymer of acrylamide / dimethylaminoethyl acrylate methyl chloride. Biochemical methane potential (BMP) assay was carried out with varying amounts of cationic polymer. The results indicated much earlier and higher biogas production rates compared to the control and increasing COD removal efficiency. Further, the low concentration of cationic polymer additive can condition the charges on the surface of the anaerobic microbes and enhance synergy of the microbe community resulting in better kinetics of hydrolysis, acidogenesis and methanogenesis. Further, the low concentration of the cationic polymer can enhance the tolerance of the microbes to the toxicity of the wastewater by conditioning the microbial community.
    • 提供了一种用于厌氧消化过程的生物气生产增强方法。 沼气生产增强的方法使用阳离子聚合物来提高将有机废物转化为沼气的效率,例如含甲烷气体。 通常使用的阳离子聚合物是丙烯酰胺/丙烯酸二甲基氨基乙酯甲基氯化物的共聚物。 用不同量的阳离子聚合物进行生物化学甲烷电位(BMP)测定。 结果表明,与控制相比,沼气生产率早于和高于COD去除效率。 此外,低浓度的阳离子聚合物添加剂可以调节厌氧微生物表面的电荷并增强微生物群落的协同作用,导致更好的水解动力学,酸生成和产甲烷生成。 此外,低浓度的阳离子聚合物可以通过调节微生物群落来增强微生物对废水毒性的耐受性。
    • 7. 发明申请
    • METHOD OF REDUCING RESIDUAL RECALCITRANT ORGANIC POLLUTANTS
    • 减少残留有机污染物的方法
    • WO2014036732A1
    • 2014-03-13
    • PCT/CN2012/081177
    • 2012-09-10
    • GENERAL ELECTRIC COMPANYWANG, SijingWANG, LeiZHANG, HaiwuXU, WeiqingZHOU, Ying
    • WANG, SijingWANG, LeiZHANG, HaiwuXU, WeiqingZHOU, Ying
    • C02F3/34C02F3/02
    • C02F3/341C02F3/02C02F3/04C02F3/106C02F3/107C02F3/108C02F3/1268C02F3/2853C02F3/348C02F2003/001C02F2003/003C02F2101/30C02F2101/327C02F2101/36C02F2101/38C02F2103/06C02F2103/365C02F2203/004C02F2305/06Y02W10/15
    • A method for reducing recalcitrant chemical oxygen demand (COD) of a liquid in a water system is provided. The method comprises pretreating the liquid in a pretreatment unit (12) to remove indigenous bacteria or microbes to a population level below which the indigenous organisms can interfere with the screened and externally introduced microorganisms. The liquid is then provided to a reactor (20) that has a filter bed (22) formed with a carrier material (26). Special microbes are screened and used to colonize the carrier material (26) to remove recalcitrant COD. A biofilm is cultured on the surface of the carrier material (26) to immobilize the screened microbes in the reactor (20). The method further comprises adding a co-substrate as the liquid enters the reactor (20) and percolating the liquid through the filter bed (22) colonized with the screened microbes to degrade at least part of the recalcitrant COD under aerobic conditions. The screened microbes comprise at least one microbial species selected from the group consisting of Bacillus, Comamonas, Arthrobacter, Micrococcus, Pseudomonas, Pediococcus, Achromobacter, Flavobacterium, Mycobacterium, Rhodanobacter, Stenotrophomonas and yeast.
    • 提供了一种降低水系中液体的难溶化学需氧量(COD)的方法。 该方法包括将预处理单元(12)中的液体预处理以将本地细菌或微生物除去至低于该水平的本地生物可能干扰被筛选和外部引入的微生物的群体水平。 然后将液体提供到具有形成有载体材料(26)的过滤床(22)的反应器(20)。 将特殊微生物筛选并用于定植载体材料(26)以除去顽固的COD。 在载体材料(26)的表面上培养生物膜,以将筛选的微生物固定在反应器(20)中。 该方法还包括当液体进入反应器(20)时加入共底物,并将液体渗透通过筛选的微生物定殖的过滤床(22),以在有氧条件下降解至少部分顽固性COD。 所筛选的微生物包含至少一种选自芽孢杆菌属,科马矛菌属,节杆菌属,微球菌属,假单胞菌属,类球菌属,无色杆菌属,黄杆菌属,分枝杆菌属,罗丹霉属,嗜麦芽寡养单胞菌属和酵母菌的微生物。
    • 10. 发明申请
    • METHOD OF REMOVING RECALCITRANT ORGANIC POLLUTANT
    • 去除重要有机污染物的方法
    • WO2012119266A1
    • 2012-09-13
    • PCT/CN2011/000359
    • 2011-03-07
    • GENERAL ELECTRIC COMPANYWANG, SijingXU, WeiqingCHENG, Zhonghong
    • WANG, SijingXU, WeiqingCHENG, Zhonghong
    • C02F9/14C02F3/34C02F3/10C02F101/30
    • C02F3/348C02F1/281C02F1/283C02F3/06C02F3/106C02F3/34Y02W10/15
    • Recalcitrant chemical oxygen demand (COD) of a liquid is reduced in a water treatment system. The method includes pretreating the liquid in a pretreatment unit to remove indigenous bacteria or microbes to a population level below which the indigenous organisms can interfere with the screened and externally introduced microorganisms. The liquid is then provided to a reactor that has a filter bed formed with a carrier material. Special microbes are screened and used to colonize the carrier material to remove recalcitrant COD. A biofilm is cultured on the surface of the carrier material to immobilize the screened microbes in the reactor. The method further includes percolating the liquid from the pretreatment unit through the filter bed colonized with the screened microbes to degrade at least part of the recalcitrant COD under aerobic conditions. In one embodiment, the filter is formed with biological granular activated carbon (GAC) as the carrier material and the screened microbes comprise at least one microbial species selected from the group consisting of Bacillus, Comamonas, Arthrobacter, Micrococcus, Pseudomonas, Pediococcus, Achromobacter, Flavobacterium, Mycobacterium, Rhodanobacter, Stenotrophomonas and Yeast .
    • 在水处理系统中,液体的化学需氧量(COD)降低。 该方法包括预处理预处理单元中的液体以将本地细菌或微生物除去至低于该水平的本地生物可能干扰被筛选和外部引入的微生物的群体水平。 然后将液体提供到具有由载体材料形成的过滤床的反应器。 筛选特殊的微生物并用于定植载体材料以除去顽固的COD。 在载体材料的表面上培养生物膜以将筛选的微生物固定在反应器中。 该方法还包括将来自预处理单元的液体渗透通过筛选微生物定殖的滤床,以在需氧条件下降解至少部分顽固性COD。 在一个实施方案中,过滤器由生物颗粒状活性炭(GAC)形成为载体材料,筛选的微生物包含至少一种选自芽孢杆菌属,科马矛菌属,节杆菌属,微球菌属,假单胞菌属,球菌属,无色杆菌属, 黄杆菌属,分枝杆菌属,杜氏杆菌属,嗜麦芽寡养单胞菌属和酵母菌属。