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Swine manure management process

机译:猪粪管理流程

摘要

MU "PROCESS OF SWINE WASTE MANAGEMENT" MV. The following report refers to the development of a PROCESS FOR MANAGE PIG WASTE, whose operational dynamics of this system make treatment compatible with the use of waste. The utilization results from the portion of the residue with the highest concentration in dry matter (sludge), retained through the separation of phases (decanter) being destined for farming. The effluent waste from the decanter with less dry matter content will undergo a treatment process (series stabilization ponds) according to the following criteria: The hydraulic model is considered in complete mixture: therefore S = S ~ o ~ / 1 = kt , where the soluble biochemically oxidizable carbonaceous concentration (BODs) is quantified, for the effluents between lagoons obeying a coefficient of determination "K" of 0.16 for the first anaerobic lagoon (A ~ 1 ~), o, 13 for the second anaerobic (A ~ 2 ~), 0.11 for the first optional (F ~ 1 ~), 0.99 for the second optional (F ~ 2 ~). In the same order, the following hydraulic retention times (TFH) follow: 40, 25, 35 and 15; for the finishing phase: 35, 25, 30 and 15 for matrix units and complete cycle. The volumetric application rate for A ~ 1 ~ = 0.15 kgDBO ~ 5 ~ / m³. day, for A ~ 2 ~ = 0.10 kgDBO ~ 5 ~ / m³. day, surface application rate for optional ponds will be 167 kgDBO ~ 5 ~ / ha. day for F ~ 1 ~ and 90 kg DBO ~ 5 ~ / ha. day. The present process for F ~ 1 ~ is 90 kgDBO ~ 5 ~ / ha.day. The present process establishes that the second anaerobic lagoon will consist of a set of baffles, causing the substrate to follow the upward and downward flow. The distance between the baffles is determined using the following criteria: the distance between the baffles causes the immersion of the liquid mass (D / 2) is half that of the rise (D). It also establishes that the second optional pond will consist of a set of baffles arranged alternately, making the hydraulic regime tend to flow in a piston. For the filtration of nutrients, a last lagoon called a filter lagoon will be inserted, containing water hyacinth, where rainwater from the facilities' gutters will also be channeled in addition to the effluent from the fourth lagoon. As an option, it is suggested that the F ~ 1 ~ effluent be introduced in continuous flow to a pond with a high rate of degradation, the effluent of which will be destined and dams containing herbivorous filtering fish.
机译:“猪废物管理过程” 。以下报告涉及猪粪管理流程的开发,该系统的运行动态使处理与废物的使用兼容。利用率是由干物质(污泥)中浓度最高的部分残留物产生的,这些残留物是通过分批用于耕作的相(dec析器)保留的。来自the水器的干物质含量较少的废水将按照以下标准进行处理(串联稳定池):•水力模型被视为完全混合:因此,S = S〜o〜/ 1 = kt,其中对于第一个厌氧池(A〜1〜)的测定系数“ K”为0.16,对于第二个厌氧池(A〜2〜),服从测定系数“ K”的泻湖之间的流出物,对可溶性生化可氧化碳含量(BODs)进行定量。 ),第一个可选项(F〜1〜)为0.11,第二个可选项(F〜2〜)为0.99。按照相同的顺序,以下液压保持时间(TFH)为:40、25、35和15;精加工阶段:矩阵单元的35、25、30和15和完整循环。体积施用率为A〜1〜= 0.15 kgDBO〜5〜/m³。一天,对于A〜2〜= 0.10 kgDBO〜5〜/m³。每天,可选池塘的表层施用量将为167 kgDBO〜5〜/ ha。一日换F〜1〜和90 kg DBO〜5〜/ ha。天。目前F〜1〜的过程为90 kgDBO〜5〜/ ha.day。本方法确定第二个厌氧泻湖将由一组挡板组成,从而导致底物跟随向上和向下的流动。挡板之间的距离使用以下标准确定:挡板之间的距离导致液体质量的浸入(D / 2)是上升(D)的一半。它还确定第二个可选池将由一组交替布置的挡板组成,从而使液压状态趋于在活塞中流动。为了过滤养分,将插入最后一个泻湖,称为滤池,其中包含水葫芦,除第四个泻湖的废水外,还将从设施的排水沟中引出雨水。作为一种选择,建议将F〜1〜废水以连续流的形式引入降解率很高的池塘,该废水的目的地是含有草食性滤鱼的水坝。

著录项

  • 公开/公告号BR9705256A

    专利类型

  • 公开/公告日2000-02-22

    原文格式PDF

  • 申请/专利权人 FABIO CRUZ MANHAES DA SILVA;

    申请/专利号BR19979705256

  • 发明设计人 FABIO CRUZ MANHAES DA SILVA;

    申请日1997-11-11

  • 分类号C05F3/00;

  • 国家 BR

  • 入库时间 2022-08-22 01:57:20

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