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    • 1. 发明授权
    • Dry processes for treating combustion exhaust gas
    • 用于处理燃烧排放气体的干燥方法
    • US5171552A
    • 1992-12-15
    • US552382
    • 1990-07-13
    • Yoshimasa MiuraEtsuo OginoMichio ItoToshio HamaShigenori OnitsukaMichio IshidaTeruyuki DoiTeruhiko Kawanabe
    • Yoshimasa MiuraEtsuo OginoMichio ItoToshio HamaShigenori OnitsukaMichio IshidaTeruyuki DoiTeruhiko Kawanabe
    • B01D53/50
    • B01D53/508F23J2215/10F23J2215/20
    • The invention provides a furnace desulfurization process which includes supplying a desulfurizing agent into a furnace or flue to cause the agent to absorb SO.sub.2 from the exhaust gas, the desulfurizing agent being a salt obtained by at least partly neutralizing a Ca desulfurizing agent with an acid; a furnace desulfurization process which includes supplying a Ca desulfurizing agent into a furnace or flue to effect a first-stage desulfurization reaction, collecting ash containing a waste of the agent having an unreacted substance enclosed therein from the exhaust gas, adding an acid to the collected ash to at least partly neutralize the unreacted portion of the agent, and recycling the ash containing the resulting salt into the furnace or flue to effect a second-stage desulfurization reaction; a dry simultaneous desulfurization-denitration process which includes supplying a Ca desulfurizing agent into a furnace or flue to effect a desulfurization reaction, collecting ash containing a waste of the agent having an unreacted substance enclosed therein from the exhaust gas, adding a denitrating reducing agent to the collected ash, and recycling the ash containing the waste desulfurizing agent and the reducing agent into the furnace or flue to effect desulfurization and denitration reactions; and a dry simultaneous desulfurization-denitration process which includes supplying a Ca desulfurizing agent into a furnace or flue to effect a desulfurization reaction, collecting ash containing a waste of the agent having an unreacted substance enclosed therein from the exhaust gas, adding an acid to the collected ash to at least partly neutralize the unreacted substance, adding a denitrating reducing agent to the ash containing the resulting salt, and recycling the ash containing the salt and the reducing agent into the furnace or flue to effect desulfurization and denitration reactions.
    • 本发明提供了一种炉式脱硫方法,其包括将脱硫剂供应到炉或烟道中,使得试剂从废气中吸收SO 2,该脱硫剂是通过用酸至少部分中和Ca脱硫剂得到的盐; 包括将Ca脱硫剂供应到炉或烟道中进行第一阶段脱硫反应的炉式脱硫方法,从废气中收集含有其中包含未反应物质的废物的灰分,向收集的烟道中加入酸 灰至少部分中和试剂的未反应部分,并将含有所得盐的灰分再循环到炉或烟道中以进行第二阶段脱硫反应; 一种干式同时脱硫脱硝方法,其包括将Ca脱硫剂供应到炉或烟道中进行脱硫反应,从废气中收集含有其中包含未反应物质的废物的灰分,将脱硝还原剂加入到 收集的灰分,并将含有废脱硫剂和还原剂的灰分回收到炉或烟道中以进行脱硫和脱硝反应; 以及干法同时脱硫脱硝工艺,其包括将Ca脱硫剂供应到炉或烟道中进行脱硫反应,从废气中收集含有其中包含未反应物质的废物的灰分,向所述废气中加入酸 收集的灰分至少部分中和未反应物质,向含有所得盐的灰分中加入脱硝还原剂,并将含有盐和还原剂的灰分再循环到炉或烟道中以进行脱硫和脱硝反应。
    • 3. 发明授权
    • Method, apparatus, program, and recording medium for evaluating ultraviolet radiation protection effect
    • 用于评估紫外线辐射防护效果的方法,设备,程序和记录介质
    • US07937227B2
    • 2011-05-03
    • US12682286
    • 2008-10-17
    • Yoshimasa MiuraMasato Hatao
    • Yoshimasa MiuraMasato Hatao
    • G06F17/40G06F17/00
    • G01N21/33
    • A method and apparatus for evaluating an ultraviolet radiation protection effect in a measurement sample is used for evaluating SPF (Sun Protection Factor). First, a temporal change of the spectral transmission spectrum in the measurement sample within a predetermined light wavelength range at predetermined wavelength intervals is measured. Second, a correlation between a light irradiating time and minimal erythema doses by predetermined lime intervals based on the temporal change of the spectral transmission spectrum is set. Third a predicted in vitro SPF in the measurement sample using a time until an accumulated minimal erythema dose that is obtained as a time integration of the minimal erythema doses based on the correlation obtained in the second step reaches 1 MED (Minimum Erythema Dose) is calculated.
    • 用于评估测量样品中的紫外线辐射防护效果的方法和装置用于评估SPF(防晒因子)。 首先,测量在预定的波长范围内的预定波长间隔的测量样本中的光谱透射光谱的时间变化。 其次,设定基于光谱透射光谱的时间变化的光照射时间与最小红斑剂量之间的相关性。 第三,计算测量样品中的预测体外SPF,使用一段时间,直到基于第二步骤中获得的相关性获得的最小红斑剂量的时间积分获得的积累的最小红斑剂量达到1 MED(最小红细胞计数) 。
    • 4. 发明授权
    • Fluidized bed incinerator
    • 流化床焚烧炉
    • US5915309A
    • 1999-06-29
    • US973853
    • 1998-04-06
    • Seiichi NakaiRyozo ShijiTakeshi MatsuiNorihiro AokiYoshimasa MiuraYusuke Okada
    • Seiichi NakaiRyozo ShijiTakeshi MatsuiNorihiro AokiYoshimasa MiuraYusuke Okada
    • F23G5/14F23G5/30F23B5/00F23D21/00
    • F23G5/30F23G5/14F23G2202/101F23G2203/502
    • The oblique bed wall (6) of the furnace main unit (1) is inclined in downward direction towards the ash discharge outlet (5). Oblique side walls (24R, 24L) are formed in the right and left side walls (1c, 1d) on the inlet (4) side of the furnace main unit (1), and fluidized bed material (S) blown up from the side fluid layers (RS, LS) is guided into the central fluid layer (CS). The fluidized bed material (S) is caused to circulate in succession from the central fluid layer (CS) at the inlet (4) side towards the central fluid layer (CS) at the ash discharge outlet (5) side towards side fluid layers (RS, LS) at the ash discharge outlet (5) side towards side fluid layers (RS, LS) at the inlet (4) side towards central fluid layer (CS) at the inlet (4) side, by dispersive air emitted from dispersive air pipes (21A, 21B, 25). In this way, the fluidized bed material (S) is caused to circulate in virtually a horizontal plane without partitioning walls. Slow combustion is conducted due to a slow fluid speed, particularly in the drying and pyrolyzing zone. Stable combustion is achieved, and generation of carbon monoxide and dioxin is suppressed.
    • PCT No.PCT / JP97 / 01376 Sec。 371日期:1998年4月6日 102(e)日期1998年4月6日PCT 1997年4月21日PCT PCT。 公开号WO97 / 41390 日期1997年11月6日炉主体(1)的倾斜床壁(6)向下倾斜朝向排灰口(5)倾斜。 倾斜侧壁(24R,24L)形成在炉主体(1)的入口(4)侧的左右侧壁(1c,1d)中,从侧面吹出的流化床材料(S) 流体层(RS,LS)被引导到中心流体层(CS)中。 使流化床材料(S)从入口(4)侧的中心流体层(CS)连续循环到在灰分排出口(5)侧朝向侧流体层( (4)侧的侧流体层(RS,LS)在入口(4)侧的中心流体层(CS)处的灰分排出口(5)侧的分散空气 空气管(21A,21B,25)。 以这种方式,使流化床材料(S)在几乎水平的平面中循环而没有分隔壁。 由于流体速度慢,特别是在干燥和热解区域,进行缓慢燃烧。 实现稳定的燃烧,抑制一氧化碳和二恶英的产生。
    • 10. 发明申请
    • ULTRAVIOLET PROTECTION EFFECT EVALUATION METHOD, EVALUATION APPARATUS, AND RECORDING MEDIUM
    • 超声波保护效应评估方法,评估装置和记录介质
    • US20130169951A1
    • 2013-07-04
    • US13823438
    • 2011-07-13
    • Yoshimasa MiuraMasato Hatao
    • Yoshimasa MiuraMasato Hatao
    • G01N21/59
    • G01N21/59G01N17/004G01N21/33
    • An evaluation method for evaluating the ultraviolet protection effect of a measurement sample applied on a substrate includes a first step of measuring, at predetermined wavelength intervals, a change over time of a spectral transmission spectrum of the measurement sample within a predetermined wavelength range by irradiating light from a light source that includes ultraviolet light, visible light, and infrared light under a predetermined irradiation condition; a second step of establishing, based on the change over time of the spectral transmission spectrum, a correlation between a light irradiation time and an erythema effective dose per unit time, which is obtained by dividing an erythema effective dose of the measurement sample by an erythema effective dose per 1 MED; and a third step of calculating an in vitro rSPF predictive value for the measurement sample on the basis of a time until a cumulative erythema effective dose, which is obtained through time integration based on the correlation, reaches 1 MED.
    • 用于评估施加在基板上的测量样品的紫外线保护效果的评估方法包括:第一步骤,以预定波长间隔,通过照射光来测量在预定波长范围内的测量样品的光谱透射光谱随时间的变化 从包含紫外光,可见光和红外光的光源在预定的照射条件下; 基于光谱透射光谱随时间的变化建立光照射时间和每单位时间的红斑有效剂量之间的相关性的第二步骤,其通过将测量样品的红斑有效剂量除以红斑 每1 MED有效剂量; 以及基于通过基于相关性的时间积分获得的累积红斑有效剂量之间的时间达到1 MED的时间来计算测量样品的体外rSPF预测值的第三步骤。