首页> 外国专利> still for avlegsna fororenande emnen in discharges in gaseous form, vetskeform and solid erhallna in the manufacture of glass or mineralfibermattor or discs or similar products

still for avlegsna fororenande emnen in discharges in gaseous form, vetskeform and solid erhallna in the manufacture of glass or mineralfibermattor or discs or similar products

机译:仍用于制造玻璃或矿物纤维,圆盘或类似产品的气体形式,维氏形式和固态埃哈尔纳形式的阿夫雷格纳·福雷南德·埃姆嫩

摘要

1429580 Reducing pollution in making resin-fibre mats SAINT GOBAIN INDUSTRIES 3 Oct 1974 [10 Oct 1973] 42998/74 Heading D1R In the production of a bonded fibre mat 23 pollution is reduced by recycling waste products by repeated passage through the mat, washing the waste products, purifying part of the waste at each cycle and transferring part of the heat resulting from fibre formation to a fluid which is then cooled. Glass fibres are produced by introducing molten material 102 into a perforated rotor and drawn downwards by an annular array of high speed hot gas jets. Alternatively the fibres are extruded from spinneret (112, Fig. 13, not shown), by directing a molten glass net (121, Fig. 14, n.s.) upon high speed rotors (123, 124) or by the action of hot gas jets upon glass rods or filaments (115, Fig. 12, n.s.). The drawn fibres are sucked onto perforated belt 15 by blower 19, distribution being achieved by oscillating nozzle 14 or by air pair of compressed air nozzles (14, Fig. 13, n.s.). Binder is applied by jets 13, preferably as an aqueous solution or dispersion of phenol formaldehyde resin, urea-formaldehyde resin, oxidised linseed oil or bitumen. Cooling water is supplied by sprays 50 situated above or below binder sprays 13 and/or below perforated belt 15 to remove the heat produced by fibre formation. (Little or no atmospheric air is drawn in for cooling, c.f. the prior art, Fig. 1, n.s.). The gases drawn through mat 23 are washed by sprays 45, by bubbling through wales in jar (48, Fig. 12, n.s.) or by counter-current contact with thin films of water flowing over dividing walls (46, Fig. 4, n.s.). Heat is also removed. Chamber 16 below the perforated belt may increase in cross section to reduce the velocity of the gas and thus collect particles of solid waste. A cyclonic or electrostatic precipitator 18 proceeds blower 19. Most of the partly purified gas is returned by duct 34 to mat forming chamber 22 and again passes through mat 23. 5% to 10% of the gas is taken to burner 39 where remaining organic impurities are connected to carbon dioxide and water and released to the atmosphere. Duct 35 leading to burner 39 may be situated in chamber 22 (Fig. 4, n.s.). Noise is reduced by absorbing panels 99, 100. The washing water collects at sump 103 and is passed through vibratory mesh filter 51 to remove fibres and insoluble binder. The filtered water is cooled by circulation through heat exchanger 105. Cooled filtered water is supplied via pump 55 to cooling sprays 50, washing means 45 binder preparation 108 and water treatment station 109. As illustrated station 109 comprises a pump 77 which raises the pressure to 16 bar, a heat exchanger 83 which raises the pressure to 80‹C, a mixer 78 in which superheated steam raises the water to 200‹C and a reactor 82 in which the treated water is kept for 2 to 4 minutes. The treated water is cooled in the heat exchanger, decompressed, centrifuged at 110 to remove binder insolubilised by the heat and returned to tank 52. In other embodiments heat is applied to the interior of a treatment tank by steam or an immersed burner or electric arc. In other embodiments the dissolved binder is removed by flocculation or bacterial action. The solid waste removed by filter 51 and centrifuge 110 is heated to 600 to 700‹C to burn organic material and frit the fibres into low volume plates which are returned to the fibre production station, or heated to 1000‹C to melt the waste fibres.
机译:1429580减少树脂纤维毡的制造污染圣戈班工业1974年10月3日[1973年10月10日] 42998/74税目D1R在生产粘合纤维毡时,通过重复地穿过该毡,洗净纤维废物,在每个循环中净化部分废物,并将纤维形成过程中产生的部分热量传递给流体,然后将其冷却。玻璃纤维是通过将熔融材料102引入多孔转子中制成的,并由高速热气流的环形阵列向下拉。或者,通过将熔融玻璃网(121,图14,ns)引导到高速转子(123、124)上或通过热气流的作用,将纤维从喷丝头(112,图13,未示出)中挤出。在玻璃棒或玻璃丝上(115,图12,ns)。抽出的纤维通过鼓风机19被抽吸到穿孔带15上,通过摆动喷嘴14或通过一对空气压缩空气喷嘴(图13中的14,未作说明)实现分配。粘合剂通过喷嘴13施加,优选作为酚醛树脂,脲醛树脂,氧化的亚麻籽油或沥青的水溶液或分散体。冷却水由位于粘合剂喷雾器13上方或下方和/或多孔带15下方或下方的喷雾器50供应,以除去由纤维形成所产生的热量。 (参见图1,n.s。,参见现有技术,很少或没有吸入大气进行冷却)。通过垫层23吸入的气体通过喷雾器45冲洗,通过罐中的威尔士鼓泡(图12,ns,48)或与流过分隔壁的水薄膜逆流接触(图4,ns,46)。 )。热量也被除去。穿孔带下方的腔室16的横截面可能会增加,以降低气体的速度,从而收集固体废物的颗粒。旋风除尘器或静电除尘器18进入鼓风机19。大部分经部分净化的气体由管道34返回垫子形成室22,并再次通过垫子23。5%至10%的气体被送入燃烧器39,在其中残留的有机杂质与二氧化碳和水相连并释放到大气中。通向燃烧器39的管道35可以位于腔室22中(图4,未示出)。通过吸收面板99、100来降低噪音。洗涤水在集水箱103处收集,并通过振动筛网过滤器51以去除纤维和不溶性粘合剂。过滤后的水通过热交换器105循环冷却。冷却后的过滤水通过泵55输送至冷却喷雾50,清洗剂45,粘合剂制剂108和水处理站109。如图所示,站109包括泵77,其将压力升高至在16巴的压力下,热交换器83将压力升高到80℃,混合器78在其中过热蒸汽将水升高到200℃,反应器82在其中保持处理过的水2-4分钟。处理后的水在热交换器中冷却,减压,在110离心以除去因热不溶的粘合剂并返回到水箱52。在其他实施方式中,通过蒸汽或浸入式燃烧器或电弧将热量施加到处理水箱的内部。 。在其他实施方案中,通过絮凝或细菌作用除去溶解的粘合剂。将通过过滤器51和离心机110去除的固体废物加热到600至700°C,以燃烧有机材料并将玻璃料烧结成小体积的板,然后返回到纤维生产站,或加热到1000°C以熔化废纤维。 。

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