首页> 外国专利> INDUSTRIAL UTILIZATION OF GARBAGE WITH EFFECTIVE RECYCLING AND WITH OPTIMISATION IN ENERGY PRODUCTION

INDUSTRIAL UTILIZATION OF GARBAGE WITH EFFECTIVE RECYCLING AND WITH OPTIMISATION IN ENERGY PRODUCTION

机译:有效回收利用和能源生产优化的垃圾工业化利用

摘要

1. Method of utilisation of garbages with effective recycling and with energy production, comprising separation of written paper in the entrance of the garbages, cutting the garbages and water flotation to separate light floating products and further separation of precipitating heavy products and composting, characterized in that after cutting the garbages to 3-5 cm and further moving and cleaning the organic mass suspended on the moving water introducing it to hydrolysis at at pH 9,5-10 and at 80-l00 degree C advancing it to biodegradability , subjecting said organic mass to anaerobic digestionin the thermophilic region and producing biogas and and sludge, collecting the sludgeand subjectingit to aerobic co-composting at 60 degree C, thus producing mixed fertilsers, humic-chemical-organic, of high value. 2. Method according to claim 1 characterized in that the separation of written paper is adopted on the incoming garbages mechanically or manually very effectively to collect the 60-80% of paper in the garbages and is processed to produce deinked pulp and at mild pulping conditions chemical pulp. 3. Method according to claim 1 characterized in that the collected floating parts in the water flotation treatment (used paper, polymers, woody mass) are pulped with 4% lime at temperature 80-100 degree C to separate the polymers after screening and the cellulocics being pulped. 4. Method according to claim 1 characterized in that the collected precipitated parts in the water flotation treatment (metals, glass and inerts) are taken out, washed magnetically, the iron metals are separated, then pulverised and subjected again to magnetic separation to collect all the iron metals and the rest is heated up to 600 degree C where the soft metals coagulate and the whole is taken into water to effectively separate the coagulated metal mass and the glass in high purity. 5. Method according to claim 1 characterized in that is added a prehydrolysis treatment before the anaerobic digestion at pH 9,5 to 10 and at temperature 80-90 degree C where are also directed the alcaline wastewaters of the paper pulping for improving the bioconvertion of contained lignocellulosics. 6. Method according to claim 5 characterized in that the prehydrolysis uses lime as alcaline reagent and is of retention time 10 to 12 hrs and the result in anaerobic digestion is an increase from 50-55 garbage bioconvertion to almost 80% biodegradation. 7. Method according to claim 1 characterized in that the wastewaters resulting from the anaerobic digestion are airstripped to collect ammonia, decanted to collect suspended matter and ionexchanged in special resins swelling in water up to 300 times to become entirely free of toxic metals. 8. Method according to claims 1 and 2 characterized in that the anaerobic digested sludge is subjected to aerobic co composting treatment at thermophilic conditions 58 62 degree C after which with destruction of organic toxicities and by aeration with the ammonia containing air from the airstripping and after addition of other needed elements fertilisers are obtained of type humic-chemical-organic of high value and biogas. 9. Method according to all claims 1 to 8 characterized in that the biogas in high volumes and fuel value is utilised to produce electric energy in combined cycle installations so that the garbages are utilised to give high values and nothing to reject.
机译:1.有效利用垃圾并产生能量的利用垃圾的方法,其特征在于,包括在垃圾的入口处分离纸质,切割垃圾并进行水浮选以分离轻浮产品,进一步分离沉淀重产品和堆肥的方法,其特征在于:在将垃圾切成3-5厘米并进一步移动并清洗悬浮在移动水上的有机物质后,将其在pH 9.5-10和80-100摄氏度下进行水解,使其可生物降解,在高温区域中大量厌氧消化并产生沼气和污泥,收集污泥并在60摄氏度下进行好氧协同堆肥,从而生产出高价值的腐殖酸-有机肥料。 2.根据权利要求1所述的方法,其特征在于,对进入的垃圾采用机械或手动非常有效的分离纸张的方法,以收集垃圾中60-80%的纸张,并在温和的制浆条件下进行处理以生产脱墨纸浆。化学纸浆。 3.根据权利要求1所述的方法,其特征在于,在水浮选处理中收集的漂浮部分(废纸,聚合物,木料)在80-100℃的温度下用4%的石灰制浆,以在筛选和纤维素分离后分离聚合物。被打浆。 4.根据权利要求1所述的方法,其特征在于,将在水浮选处理中收集的沉淀部分(金属,玻璃和惰性气体)取出,磁力洗涤,分离出铁金属,然后粉碎并再次进行磁分离以收集全部将铁金属和其余金属加热到600摄氏度,在此温度下,软金属凝结,然后将其全部放入水中,以有效分离高纯度的凝结金属块和玻璃。 5.根据权利要求1所述的方法,其特征在于,在pH值为9.5至10,温度为80-90℃的厌氧消化之前,添加预水解处理,其中还引导纸浆的碱性废水以改善纸浆的生物转化。包含木质纤维素。 6.根据权利要求5所述的方法,其特征在于,所述预水解使用石灰作为碱性试剂,并且保留时间为10至12小时,并且厌氧消化的结果是从50-55%的垃圾生物转化率增加到几乎80%的生物降解率。 7.根据权利要求1所述的方法,其特征在于,将所述厌氧消化所产生的废水进行空气汽提以收集氨,倾析以收集悬浮物,并与在水中溶胀达300倍的完全溶解有毒金属的特殊树脂进行离子交换。 8.根据权利要求1和2所述的方法,其特征在于,所述厌氧消化的污泥在58-62℃的嗜热条件下进行好氧堆肥处理,此后破坏有机毒性,并通过来自汽提的含氨空气曝气,然后通过添加其他需要的元素,可以得到高价值的腐殖化学有机物和沼气。 9.根据权利要求1至8中的所有权利要求所述的方法,其特征在于,在联合循环设施中,利用具有高体积和燃料价值的沼气来产生电能,从而利用垃圾来提供高价值而没有被拒绝的东西。

著录项

  • 公开/公告号EA000845B1

    专利类型

  • 公开/公告日2000-06-26

    原文格式PDF

  • 申请/专利权人 INNOVAL MANAGEMENT LIMITED;

    申请/专利号EA19980000612

  • 发明设计人 VALKANAS GEORGE G.;VLYSSIDES APOSTOLOS G.;

    申请日1996-12-17

  • 分类号B03B9/06;C05F17/00;C05F17/02;C12P5/02;D21B1/02;

  • 国家 EA

  • 入库时间 2022-08-22 01:56:35

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