城市污水处理厂工程设计
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本设计污水处理厂综合设计包括15个图纸,十分全面,具体详见报告后附图。
本报告附图全面详细。
图纸内容如下:A2O池,初沉池,幅流式二沉池,隔栅,工艺简单图,工艺流程图(高程图),回转耙式格栅除污机图,平面布置图,污泥浓缩池,厌氧消化池,钟式沉砂池等。
全为CAD制图。
下载后复制放大或打印可看清!题目20000m3/d城市污水处理厂综合设计专业: 环境工程年级: 2005级学号: 3105001286姓名: 莫笑伟指导教师:2008年12 月摘要我国水体污染主要来自两方面,一是工业发展超标排放工业废水,二是城市化中由于城市污水排放和集中处理设施严重缺乏,大量生活污水未经处理直接进入水体造成环境污染。
工业废水近年来经过治理虽有所减少,但城市生活污水有增无减,占水质污染的51%以上。
我国水体污染主要来自两方面,一是工业发展超标排放工业废水,二是城市化中由于城市污水排放和集中处理设施严重缺乏,大量生活污水未经处理直接进入水体造成环境污染。
工业废水近年来经过治理虽有所减少,但城市生活污水有增无减,占水质污染的51%以上。
本设计要求处理水量为20000m3/d的城市生活污水,设计方案针对已运行稳定有效的A2/O活性污泥法工艺处理城市生活污水。
A2O工艺由于不同环境条件,不同功能的微)能生物群落的有机配合,加之厌氧、缺氧条件下,部分不可生物降解的有机物(CODNB被开环或断链,使得N、P、有机碳被同时去除,并提高对COD的去除效果。
它可以同NB--时完成有机物的去除,硝化脱氮、磷的过量摄取而被去除等功能,脱氮的前提是NH3N应完全硝化,好氧池能完成这一功能,缺氧池则完成脱氮功能。
厌氧池和好氧池联合完成除磷功能。
关键词:城市生活污水,活性污泥,A2/O目录摘要 (III)目录 (IV)第一章设计概述 ······································································- 7 -1设计任务 ······································································- 7 - 2设计原则 ······································································- 7 - 3设计依据 ······································································- 8 - 第二章工艺流程及说明 ·····························································- 8 -1工艺方案分析 ································································- 8 - 2工艺流程 ······································································- 9 - 3流程各结构介绍 ·····························································- 9 -3.1格栅······························································································· - 9 -3.2沉砂池··························································································- 10 -3.3初沉池··························································································- 10 -3.4生物化反应池··············································································- 10 -3.5二沉池··························································································- 12 -3.6浓缩池··························································································- 12 - 第三章构筑物设计计算 ··························································· - 12 -1格栅 ·········································································· - 12 -1.1设计说明······················································································- 12 -1.2设计计算······················································································- 13 -2沉砂池 ······································································· - 16 -2.1设计说明······················································································- 16 - 3初沉池 ······································································· - 17 -3.1设计说明······················································································- 17 -3.2设计计算······················································································- 17 - 4生化池 ······································································· - 19 -4.1设计说明······················································································- 19 -4.2设计计算······················································································- 19 - 5二沉池 ······································································· - 26 -5.1设计说明······················································································- 26 -5.2设计计算······················································································- 26 - 6液氯消毒 ···································································· - 29 -6.1设计说明······················································································- 29 -6.2设计计算······················································································- 29 - 7污泥浓缩池 ································································· - 30 -7.1设计说明······················································································- 30 -7.2设计计算······················································································- 30 -8 污泥消化池 ································································· - 31 -8.1设计说明······················································································- 31 -8.2设计计算······················································································- 32 - 9浓缩污泥提升泵房 ························································ - 38 -9.1设计选型······················································································- 38 -9.2提升泵房······················································································- 38 -9.3污泥回流泵站··············································································- 38 -10污泥脱水间 ······························································· - 39 -10.1设计说明······················································································- 39 -11鼓风机房 ·································································· - 39 - 12恶臭处理系统 ···························································· - 39 -12.1设计说明······················································································- 39 -12.2设计计算······················································································- 39 -12.3风机选型······················································································- 40 - 第四章污水处理厂总体布置 ····················································· - 41 -1总平面布置 ································································· - 41 -1.1总平面布置原则··········································································- 41 -1.2总平面布置结果··········································································- 41 -2高程布置································································································- 42 -2.1高程布置原则··············································································- 42 - 第五章参考文献 ···································································· - 42 -第一章设计概述1设计任务本次课程设计的主要任务是完成某城市污水厂的A2/O工艺设计处理生活污水,处理水量为20000m3/d,按近期规划人口10万人计算(自定)。
中小型城镇污水处理工程
设计水量2.5万m3/d,进水水质BOD5:170~190mg/L,SS:220~270mg/L,COD Cr:330~380mg/L,NH4-N:35mg/L。
污水排放执行《污水综合排放标准》(GB8978-96)一级标准。
技术工作要求:
1、污水处理系统方案的比较
(1)污水处理系统规模确定
(2)污水处理方法、流程比较和污水处理构筑物型式的选择。
(3)污泥处理方法、流程比较和污泥处理构筑物型式的选择。
(4)污水处理系统投资及运行费用估算。
(5)污水处理系统方案综合比较。
2、污水处理系统设计计算
(1)污水处理构筑物的设计计算。
(2)污泥处理构筑物的设计计算。
(3)污水处理系统平面布置。
(4)污水处理系统高程计算。
3、设计图纸的绘制
(1)污水处理厂平面布置图。
(2)污水、污泥处理工艺流程图。
(3)主要构筑物工艺设计图。
(4)主要单体构筑物大样图。
4、污水处理系统概预算
(1)污水处理厂土建工程概算表。
(2)污水处理厂设备、安装工程概算表。
(3)污水处理厂其它工程费用概算表。
(4)污水处理厂总概算表。
5、设计说明书、计算书编制
(1)设计说明书编制。
(2)设计计算书编制。
浅谈城市污水处理工程的设计与实施摘要:针对目前各地在兴建城市污水处理工程的过程中所暴露出来的问题,从管网体制及厂址的选择和技术、污泥处理等角度进行剖析,并对应注意的环节陈述了笔者的看法。
关键词:污水处理工程设计与实施一、污水收集系统1.1 排水体制排水体制是污水处理厂设计所面临的首要问题,它不仅涉及工程投资、环境保护、工程实施的难易程度,还直接影响污水处理厂的工艺选择。
合理选择排水体质,是进行排水系统规划、污水管网设计中一个十分复杂而重要的任务,它涉及到城市的规划、环境规划、地形条件、气候条件、水体分布等多项因素。
应根据城镇和工业企业规划、当地降雨情况和排放标准、排水设施、污水处理和利用情况、地形和水体等条件综合确定。
选择合适的排水体制将有利于减少污水处理系统的投资,提高减污效率和环境效益。
我国的中小城市在长期发展过程中,由于受投资因素的限制及发展模式的影响,现状建成区多为雨污合流制。
合流制区域面积至少占建成区面积的80%以上,而且八十年代以前的建成区,建筑密集,各种地下管线拥挤,要改造为分流制,需增设一套污水管网系统,难度非常大。
结合近年来国内城市污水处理厂及排水系统的建设情况,我国各城镇排水体制宜按如下原则进行:对于新城区、新开发区、采用完全分流制的排水系统;对于改造难度很大的大中城市的旧城区合流制排水系统,可维持合流制排水系统,合理确定截留倍数;在有多个污水处理分区的城镇,每个分区内部的排水体制宜统一;对规划为分流制,目前实施不完全分流或有混接情况的排水分区,可按近期分流集污和合流截污并存,远期逐步改造成完全分流排水体制;对现状为合流制排水系统的小城镇,现状区域维持合流制排水系统,合理确定截留倍数,新建区采用分流制排水系统,在规模达到一定程度时尽可能分建污水处理系统。
1.2 污水收集系统优先考虑的问题⑴编制城镇污水专项规划;⑵重视管网配套建设;⑶优先完善集污主干管的建设:⑷污染物总量控制指标;⑸截留雨水的处理;⑹建立多元化畅通的资金渠道;⑺采用合适新管材和施工方案。
本设计污水处理厂综合设计包括15个图纸,十分全面,具体详见报告后附图。
本报告附图全面详细。
图纸内容如下:A2O池,初沉池,幅流式二沉池,隔栅,工艺简单图,工艺流程图(高程图),回转耙式格栅除污机图,平面布置图,污泥浓缩池,厌氧消化池,钟式沉砂池等。
全为CAD制图。
下载后复制放大或打印可看清!题目20000m3/d城市污水处理厂综合设计专业: 环境工程年级: 2005级学号: 3105001286姓名: 莫笑伟指导教师:2008年12 月摘要我国水体污染主要来自两方面,一是工业发展超标排放工业废水,二是城市化中由于城市污水排放和集中处理设施严重缺乏,大量生活污水未经处理直接进入水体造成环境污染。
工业废水近年来经过治理虽有所减少,但城市生活污水有增无减,占水质污染的51%以上。
我国水体污染主要来自两方面,一是工业发展超标排放工业废水,二是城市化中由于城市污水排放和集中处理设施严重缺乏,大量生活污水未经处理直接进入水体造成环境污染。
工业废水近年来经过治理虽有所减少,但城市生活污水有增无减,占水质污染的51%以上。
本设计要求处理水量为20000m3/d的城市生活污水,设计方案针对已运行稳定有效的A2/O活性污泥法工艺处理城市生活污水。
A2O工艺由于不同环境条件,不同功能的微)能生物群落的有机配合,加之厌氧、缺氧条件下,部分不可生物降解的有机物(CODNB被开环或断链,使得N、P、有机碳被同时去除,并提高对COD的去除效果。
它可以同NB--时完成有机物的去除,硝化脱氮、磷的过量摄取而被去除等功能,脱氮的前提是NH3N应完全硝化,好氧池能完成这一功能,缺氧池则完成脱氮功能。
厌氧池和好氧池联合完成除磷功能。
关键词:城市生活污水,活性污泥,A2/O目录摘要 (III)目录 (IV)第一章设计概述 ······································································- 7 -1设计任务 ······································································- 7 - 2设计原则 ······································································- 7 - 3设计依据 ······································································- 8 - 第二章工艺流程及说明 ·····························································- 8 -1工艺方案分析 ································································- 8 - 2工艺流程 ······································································- 9 - 3流程各结构介绍 ·····························································- 9 -3.1格栅······························································································· - 9 -3.2沉砂池··························································································- 10 -3.3初沉池··························································································- 10 -3.4生物化反应池··············································································- 10 -3.5二沉池··························································································- 12 -3.6浓缩池··························································································- 12 - 第三章构筑物设计计算 ··························································· - 12 -1格栅 ·········································································· - 12 -1.1设计说明······················································································- 12 -1.2设计计算······················································································- 13 -2沉砂池 ······································································· - 16 -2.1设计说明······················································································- 16 - 3初沉池 ······································································· - 17 -3.1设计说明······················································································- 17 -3.2设计计算······················································································- 17 - 4生化池 ······································································· - 19 -4.1设计说明······················································································- 19 -4.2设计计算······················································································- 19 - 5二沉池 ······································································· - 26 -5.1设计说明······················································································- 26 -5.2设计计算······················································································- 26 - 6液氯消毒 ···································································· - 29 -6.1设计说明······················································································- 29 -6.2设计计算······················································································- 29 - 7污泥浓缩池 ································································· - 30 -7.1设计说明······················································································- 30 -7.2设计计算······················································································- 30 -8 污泥消化池 ································································· - 31 -8.1设计说明······················································································- 31 -8.2设计计算······················································································- 32 - 9浓缩污泥提升泵房 ························································ - 38 -9.1设计选型······················································································- 38 -9.2提升泵房······················································································- 38 -9.3污泥回流泵站··············································································- 38 -10污泥脱水间 ······························································· - 39 -10.1设计说明······················································································- 39 -11鼓风机房 ·································································· - 39 - 12恶臭处理系统 ···························································· - 39 -12.1设计说明······················································································- 39 -12.2设计计算······················································································- 39 -12.3风机选型······················································································- 40 - 第四章污水处理厂总体布置 ····················································· - 41 -1总平面布置 ································································· - 41 -1.1总平面布置原则··········································································- 41 -1.2总平面布置结果··········································································- 41 -2高程布置································································································- 42 -2.1高程布置原则··············································································- 42 - 第五章参考文献 ···································································· - 42 -第一章设计概述1设计任务本次课程设计的主要任务是完成某城市污水厂的A2/O工艺设计处理生活污水,处理水量为20000m3/d,按近期规划人口10万人计算(自定)。
长春市东南污水处理厂工程设计长春市东南污水处理厂工程设计1. 引言随着长春市人口的增加和城市化进程的推进,污水处理成为了一项紧迫的任务。
长春市东南污水处理厂的工程设计成为了一个重要的项目,其目标是提供高效、可靠的污水处理设施,保护环境和人民健康。
本文就该工程的设计进行详细阐述。
2. 工程背景长春市东南污水处理厂位于长春市东南部,总占地面积为XXX平方米。
该区域是长春市人口密集的地区,每天产生的污水量大约为XXX立方米,且污水中含有高浓度的有机物和悬浮物等。
因此,东南污水处理厂需要具备高处理能力和适应性。
3. 污水处理工艺选择在工程设计初期,我们经过多次沟通和评估,最终选择了A2O (缺氧-缺氧-氧化)工艺作为主要处理工艺。
该工艺具有处理效果好、运行成本低等优点,非常适合处理这种高浓度有机物的污水。
此外,我们还引入了MBR(膜生物反应器)工艺作为后处理工艺,以进一步提高出水水质。
4. 设计方案根据预先确定的处理能力需求和输入水质的特点,我们设计了一套完整的处理系统。
整个系统包括了预处理、生物处理、沉淀池、膜生物反应器和消毒等单元。
4.1. 预处理单元预处理单元主要负责去除污水中的大颗粒悬浮物和沉积物。
我们采用了集水井的方式,通过物理方法将大颗粒物质去除,并使用格栅和沉砂池进一步清除杂质。
这样可以减轻后续处理单元的负担,提高系统整体效果。
4.2. 生物处理单元生物处理单元是整个工程的核心部分,用于降解污水中的有机物和氮磷等营养物质。
我们设计了一套A2O工艺的生物反应器,通过控制缺氧、缺氧和氧化的区域,实现有机物的高效降解。
在该单元中,微生物扮演着重要的角色,其代谢活动可高效地去除污水中的有机物。
4.3. 沉淀池沉淀池负责分离污水中的固体物质和生物芽孢等。
在设计中,我们考虑到污水中的悬浮物较多,因此采用了大面积沉淀池,以提高沉降效果和固液分离效果。
4.4. MBR单元MBR单元是后处理单元,通过使用微孔膜对污水进行过滤,有效地去除细菌和悬浮颗粒物,并进一步提高出水质量。
城市污水处理厂设计城市污水处理厂设计是一个综合性极强的系统工程,涉及的学科多,相关部门多,其中任何一个环节不合理都会给工程设计带来影响和造成不同程度的损失。
污水处理厂设计,直接关系到建设费用和运行费用的多少、处理效果的好坏、占地面积的大小、管理上的方便与否等关键问题。
因此,在进行污水处理厂设计时,必须做好方案的比较,以确定最佳方案。
一、城市污水处理厂设计(一)基本条件1处理规模:处理规模的确定主要与下列因素有关:城市人口包括常住人口和流动人口。
通常是根据城市总体规划近、远期及远景人口预测来确定的。
当城市总体规划编制年限较早,尚未修编或者修编中,需对现状人口核实并进行合理的分析和预测。
同时,确定人口时,要特殊注意旅游城市在旅游旺季浮现人口峰值的特点及对城市水量变化系统的影响。
城市性质及经济水平城市所在地域、自然条件、经济发达程度、人民生活习惯及住房条件不同,城市居民用水量标准不同,于是城市污水量亦不同。
城市排水体制城市排水体制分为分流制和合流制。
普通新建城市、扩建新区、新建开辟区及经济条件较好的城市宜采用分流制;一些大中型城市中已建成的旧城区由于历史原因,普通为合流制,可改造成截流式合流制。
根据城市具体情况,同一城市的不同地区可采用不同的排水体制。
城市排水体制的选择直接影响污水量规模,当采用分流制时,设计污水量全部为城市污水(包括生活污水和工业废水等),当采用截流式合流制和分流制组合系统时,必须考虑截流式合流系统中排入的雨水量,该雨水量与设计截流倍数有关,应进行科学分析后合理确定。
工业废水量由于城市结构各异,工业类型和工业比重不同,于是,工业废水量及水质量不相同。
根据“城市污水处理工程项目建设标准”,工业废水经工厂内自行处理,达到“污水排入城市下水道水质标准”(CJ3082-1999)后,优先考虑纳入城市污水采集系统,与城市生活污水合并处理。
因此,工业废水量是城市污水处理厂确定处理规模的重要组成部份,必须对其废水量进行充分调查研究,合理确定工业废水量。
环境工程课程设计题目2万吨/日城市污水处理厂的初步设计院系材料科学与工程学院专业环境工程姓名陈强年级大四上学期指导教师廖润华、成岳、苏小丽摘要本次课程设计的题目为某城市污水处理厂初步设计,主要任务是完成该污水处理厂的平面布置、高程布置和各处理构筑物的初步设计。
初步设计要完成设计说明书一份,污水处理厂平面布置图1张、污水处理构筑物高程布置图1张。
该污水处理厂工程规模为2万吨/日,进水水质为:CODCr =200mg/L,BOD5=150mg/L,SS=200mg/L,氨氮=30mg/L,磷酸盐(以P计)=4.0mg/L。
本次设计所选择的A2O工艺,具有良好的脱氮除磷功能。
该污水处理厂的污水处理流程为:污水从粗格栅到污水提升泵房,再从泵房到细格栅,然后到沉砂池,进入初沉池再进入生物池(即A2O反应池),再从生物池进入二沉池,污水再经过接触消毒池后排入自然水体;污水处理厂处理后的出水水质执行《城镇污水处理厂污染物排放标准》(GB18918-2002)一级标准的A标准。
关键词:A2O工艺;脱氮除磷;污水处理目录摘要 (2)1设计任务书 (6)1.1工程设计资料 (6)1.2设计任务 (7)1.3 基本要求 (7)1.4毕业设计图纸内容及张数 (7)2 设计说明书 (8)2.1城市污水来源、水量及水质特点分析 (8)2.1.1城市污水来源 (8)2.1.2城市污水水量 (9)2.1.3城市污水水质特点 (9)2.2污水处理方案的选择 (10)2.2.1城市污水主要处理方法 (10)2.2.2污水处理方案的选择 (12)2.3污水处理工艺原理及工程说明 (13)2.3.1粗格栅 (13)2.3.2泵房和集水池 (15)2.3.2.1泵房 (15)2.3.2.2集水池 (15)2.3.3细格栅 (16)2.3.4沉砂池 (16)2.3.5配水井 (18)2.3.6初沉池 (19)2.3.7生化池 (20)2.3.8配水井 (21)2.3.9二沉池 (22)2.3.10接触消毒池 (23)3设计计算书 (24)3.1粗格栅间 (24)3.1.1设计参数 (24)3.1.2设计计算 (24)3.2 集水池和泵房 (26)3.2.2 集水池设计计算 (26)3.2.3水泵扬程计算 (27)3.3细格栅 (28)3.3.1设计参数 (28)3.3. 2设计计算 (28)3.4沉砂池 (29)3.4.1 设计参数 (29)3.4.2设计计算 (30)3.5配水井 (32)3.5.1设计参数 (32)3.5.2设计计算 (33)3.6初沉池 (34)3.6.1设计参数 (34)3.6.2 设计计算 (34)3.7厌氧池 (36)3.7.1 设计参数 (36)3.7.2设计计算 (36)3.8缺氧池 (37)3.8.1 设计参数 (37)3.8.1 设计计算 (37)3.9曝气池 (37)3.9.1设计参数设计参数 (37)3.9.2污水处理程度的计算 (38)3.9.3曝气池的计算与各部位尺寸的确定 (38)3.10配水井 (41)3.10.1设计参数 (41)3.10.2设计计算 (41)3.11二沉池 (42)3.11.1设计参数 (42)3.11.2 设计计算 (42)3.12 消毒池 (44)3.12.1设计参数 (44)3.13高程计算 (46)结论 (48)参考文献 (48)附录 (49)1设计任务书1.1工程设计资料(1)工程概况某城市拟筹建城市污水处理厂,废水量为2万吨/日。
城市污水处理厂设计与建设标准一、前言城市污水处理是城市环境保护的重要组成部分,污水处理厂的设计与建设标准是确保污水处理厂正常运行的关键。
本文将从污水处理厂的设计和建设两个方面进行详细讲解。
二、污水处理厂的设计标准1.设计原则污水处理厂的设计应符合以下原则:(1)科学性:设计应符合现代化、科学化、可操作性的要求。
(2)可靠性:污水处理厂的设计应具有可靠性,确保设备的安全、稳定、长期运行。
(3)经济性:污水处理厂的设计应具有经济性,减少投资、降低运营成本。
(4)适应环境:污水处理厂的设计应考虑周围环境的影响,确保对周围环境不会造成污染。
2.设计要求污水处理厂的设计应满足以下要求:(1)处理能力:污水处理厂的设计应根据所处城市的人口规模和污水排放量确定其处理能力。
(2)处理工艺:污水处理厂的设计应根据污水的水质、水量、污染物种类和浓度等因素确定处理工艺。
(3)设备选型:污水处理厂的设计应根据处理工艺的要求,选用适合的设备进行处理,确保设备的质量和可靠性。
(4)建筑布局:污水处理厂的设计应进行合理的建筑布局,确保各处理单元之间的联系顺畅,方便操作和维护。
(5)环境保护:污水处理厂的设计应符合环保要求,减少对周围环境的污染。
3.设计内容污水处理厂的设计应包括以下内容:(1)污水处理工艺流程图。
(2)处理单元的设计参数和设备选型。
(3)建筑布局图和设备布置图。
(4)电气控制系统和通讯系统的设计。
(5)环保设施的设计。
三、污水处理厂的建设标准1.建设原则污水处理厂的建设应符合以下原则:(1)安全性:污水处理厂的建设应符合安全生产的要求,确保工人人身安全。
(2)环保性:污水处理厂的建设应符合环保要求,减少对周围环境的影响。
(3)可靠性:污水处理厂的建设应具有可靠性,确保设备的安全、稳定、长期运行。
(4)经济性:污水处理厂的建设应具有经济性,减少投资、降低运营成本。
2.建设要求污水处理厂的建设应满足以下要求:(1)建设规模:污水处理厂的建设规模应根据所处城市的人口规模和污水排放量确定。
1.总论随着科学的发展、时代的进步、人口的迅猛增长,人类赖以生存和发展的环境受到污染,水资源短缺和水环境污染的程度日益加剧,使得城市污水的有效回收利用成为一项紧迫的任务。
水资源的污染及短缺是当今社会面临的一个重大问题。
据统计,2000年我国城市污水排放量已达332亿立方米,其中绝大部分水未经有效处理而排入江河湖海。
全国90%以上的城市水域受到不同程度的污染,近50%的重点城镇的集中饮用水源不符合标准。
我国北方城市大部分受到资源型缺水困扰,南方多水地区由于受到不同程度的污染,已经呈现缺水趋势。
因此,增加污水处理比例和将污水处理之后再回用是今后我国城市污水处理的趋势。
城市污水包括生活污水、工业废水和径流污水等,由城市排水管网汇集并输送到污水处理厂进行处理。
城市污水处理工艺因地制宜采用多种形式,要根据城市污水的利用或排放去向同时考虑水体的自然净化以及污水在利用过程中的净化作用.确定废水的处理程度及相应的处理工艺。
处理后的污水,无论用于工业、农业或外排,均应符合国家规定标准。
城市污水处理分为三个级别,即一级处理(机械处理)、二级处理(生物处理)、三级处理(高级处理)。
一级处理主要采用格栅、沉砂池、沉淀池等构筑物,去除污水中不溶解的悬浮物等。
二级处理主要去除一级沉淀池出水中的胶体和溶解性有机物。
典型设备是生物曝气池(或生物滤池)和二次沉淀池。
三级处理主要去除二级出水中营养物(氮和磷)及其他难降解物质。
主要方法有絮凝、过滤、吸附、离子交换等物化法。
三级处理的目的是避免水体富营养化或回用水。
1.1设计任务和内容1.1.1工程设计的目的工程设计是环境工程专业重要的实践教学环节,教学时间为三周。
工程设计以城市污水处理厂工艺为主线,要求学生利用所学知识,在教师的指导下提出工艺设计方案,进行工艺设计计算,编制设计说明文件,绘制工艺条件图等系统训练。
1.1.2设计题目某城市污水处理厂工艺设计1.1.3设计要求(1)完成主要处理构筑物的设计布置;(2)工艺选择、设备选型、技术参数、性能、详细说明;(3)提交的成品:设计说明书、单元设备工艺条件图、污水处理厂平面布置图。
1.1.4设计内容(1)进行一般水处理构筑物的工艺设计计算;(2)编制设计说明文件;(3)设计图纸:污水处理厂平面图,绘制单元设备工艺条件图。
1.1.4设计任务设计进、出水水质及排放标准项目CODcr(mg/L)BOD5(mg/L)SS(mg/L)NH3-N(mg/L)进水水质CODcr=430mg/L BOD5=220mg/L SS=260mg/L NH3-N=16mg/L出水水质CODcr <70mg/L BOD5<20mg/L SS<30mg/L NH3-N<5mg/L1.2基本资料(1)污水水量与水质:污水处理水量:10万3m污水水质:CODcr=430mg/L BOD5=220mg/L SS=260mg/L NH3-N=16mg/L (2)处理要求:污水经过二级处理后应符合以下具体要求:CODcr <70mg/L BOD5<20mg/L SS<30mg/L NH3-N<5mg/L(3)处理工艺流程污水处理具体流程如下:污水→格栅→污水泵房→沉砂池→初沉池→曝气池(污泥回收)→二沉池→出水(4)厂区地形污水厂址区域海拔标高在64—66m之间,平均地面标高为64.5m。
平均地面坡度0.3%0—0.5%,地形西北高、东南低。
厂区面积为东西厂380m,南北长280m。
2.污水处理工艺流程及构筑物说明2.1污水处理工艺流程处理工艺具体流程如下:污水→粗格栅→污水泵房→细格栅→沉砂池→初沉池→氧化沟→出水2.2主要构筑物说明2.2.1格栅格栅是一组(或多组)相平行的金属栅条与框架组成,倾斜安装在进水的渠道,或进水泵站集水井的进口处,以拦截污水中较大的悬浮物及杂质,以保证后续处理构筑物或设备的正常工作. 按格栅栅条间距的大小不同,格栅分为粗格栅、中格栅和细格栅3类。
按格栅的清渣方法,有人工格栅和机械格栅两种。
格栅设备一般用于污水处理的进水渠道上或提升泵站集水池的进口处,主要作用是去除污水中较大的悬浮或漂浮物,以减轻后续水处理工艺的处理负荷,并起到保护水泵、管道、仪表等作用。
当拦截的栅渣量大于0.2m3/d时,一般采用机械清渣方式;栅渣量小于0.2m3/d时,可采用人工清渣方式,也可采用机械清渣方式。
本设计采用机械格栅。
本设计格栅为平面型,倾斜安装机械格栅。
格栅过栅流速不宜小于0.6m/s,不宜大于1.5m/s。
栅前水深应与入厂污水管规格相适应。
2.2.2沉砂池沉砂池一般是设在污水处理厂生化构筑物之前的泥水分离的设施。
分离的沉淀物质多为颗粒较大的砂子,沉淀物质比重较大,无机成分高,含水量低。
污水在迁移、流动和汇集过程中不可避免会混入泥砂。
污水中的砂如果不预先沉降分离去除,则会影响后续处理设备的运行。
最主要的是磨损机泵、堵塞管网,干扰甚至破坏生化处理工艺过程。
本设计选用平流式沉砂池,两座并行运行,水力停留时间宜选50s,沉砂量可选0.05-0.1L/m3,贮砂时间为两天,连续排砂。
2.2.3初沉池沉淀池一般是在生化前或生化后泥水分离的构筑物,多为分离颗粒较细的污泥。
在生化之前的称为初沉池,沉淀的污泥无机称为较多,污泥含水率相对于二沉池污泥低些。
辐流式,表面负荷为q=2.0—3.0 m3/(m2·h),沉淀时间为1.5—2h,SS去除率50-60%。
2.2.4曝气池利用活性污泥法进行污水处理的构筑物。
池内提供一定污水停留时间,满足好氧微生物所需要的氧量以及污水与活性污泥充分接触的混合条件。
曝气池主要由池体、曝气系统和进出水口三个部分组成。
池体一般用钢筋混凝土筑成,平面形状有长方形、方形和圆形等。
曝气方法主要有鼓风曝气和机械曝气。
本设计采用鼓风曝气,污泥负荷为0.3kg BOD5/kgMLVSS·d,SVI值选120-150ml/g,污泥浓度不宜大于3500mg/L。
2.2.5曝气池利用卡鲁塞尔(Carrousel)氧化沟的说明氧化沟(Oxidation Ditch)是本世纪50年代由荷兰工程师发明的一种新型活性污泥法,其曝气池呈封闭的沟渠形,废水和活性污泥的混合液在其中不断循环流动,因此被称为“氧化沟”。
实际上它是活性污泥法的一种变型,因为废水和活性污泥的混合液在环状的曝气渠道中不断循环流动,有人称其为“循环曝气池”、“无终端的曝气系统”。
自1954年荷兰建成第一座间歇运行的氧化沟以来,氧化沟在欧洲、北美、南非及澳大利亚得到了迅速的推广应用。
至1985年,美国已建有553座氧化沟污水处理厂,荷兰216座,西德226座,丹麦300座。
其工艺和构造也有了很大的发展和进步,处理能力不断提高,至今已有规模达65万m3/d的大型氧化沟处理厂;处理范围不断扩大,不仅能处理生活污水,也能处理工业废水、城市废水,而且在脱氮除磷方面表现了极好的性能。
我国近年来在氧化沟技术的研究及推广应用方面有了很迅速的发展。
尤其在城市污水处理厂中获得应有的推广。
(1)氧化沟的技术特征氧化沟污水处理技术能在近五十年来取得迅速的发展,主要是由于它出水水质好,运行稳定,管理方便,并具有区别于传统活性污泥法的一系列技术特征,现概括如下:1.采用的技术参数:氧化沟常用的技术参数如下:有机物容积负荷0.2~0.4 kgBOD5/m3·d有机物污泥负荷0.05~0.15 kgBOD5/kgVSS·d水力停留时间10~24hr污泥龄10~30day活性污泥浓度2000~6000 mg/L出水水质BOD5 10~15mg/LSS 10~20mg/LNH3-N 1~3mg/L氧化沟所采用的有机物负荷和水力停留时间与延时曝气法接近,但所取得的出水水质较好。
当然,氧化沟也可采用不同于上列的技术参数。
如采用较高的有机物负荷、较短的水力停留时间,使其运行的特征接近于高负荷活性污泥法或其他类型的活性污泥法。
2.采用的处理流程:以氧化沟处理城市污水时,可不设初次沉淀池,悬浮状有机物可在氧化沟中得到好氧稳定,这比设初沉池及污泥稳定池要经济。
由于氧化沟所采用的污泥龄很长,其剩余污泥量少于一般活性污泥法,而且已经得到好氧稳定,不需再经污泥消化处理。
为防止无机沉渣在氧化沟中积累,原污水应先经格栅及沉砂池预处理。
一般,氧化构污水厂的处理流程如图1-1所示:2.2.6氧化沟的优缺点分析氧化沟优点:一体化氧化沟除一般氧化沟所具有的优点外,还有以下独特的优点:①工艺流程短,构筑物和设备少,不设初沉池、调节池和单独的二沉池;②污泥自动回流,投资少、能耗低、占地少、管理简便;③造价低,建造快,设备事故率低,运行管理工作量少;④固液分离效果比一般二次沉淀池高,使系统在较大的流量浓度范围内稳定运行。
氧化沟缺点:尽管氧化沟具有出水水质好、抗冲击负荷能力强、除磷脱氮效率高、污泥易稳定、能耗省、便于自动化控制等优点。
但是,在实际的运行过程中,仍存在一系列的问题。
1.污泥膨胀问题当废水中的碳水化合物较多,N、P含量不平衡,pH值偏低,氧化沟中污泥负荷过高,溶解氧浓度不足,排泥不畅等易引发丝状菌性污泥膨胀;非丝状菌性污泥膨胀主要发生在废水水温较低而污泥负荷较高时。
微生物的负荷高,细菌吸取了大量营养物质,由于温度低,代谢速度较慢,积贮起大量高粘性的多糖类物质,使活性污泥的表面附着水大大增加,SVI值很高,形成污泥膨胀。
针对污泥膨胀的起因,可采取不同对策:由缺氧、水温高造成的,可加大曝气量或降低进水量以减轻负荷,或适当降低MLSS(控制污泥回流量),使需氧量减少;如污泥负荷过高,可提高MLSS,以调整负荷,必要时可停止进水,闷曝一段时间;可通过投加氮肥、磷肥,调整混合液中的营养物质平衡(BOD5:N:P=100:5:1);pH值过低,可投加石灰调节;漂白粉和液氯(按干污泥的0.3%~0.6%投加),能抑制丝状菌繁殖,控制结合水性污泥膨胀。
2.泡沫问题由于进水中带有大量油脂,处理系统不能完全有效地将其除去,部分油脂富集于污泥中,经转刷充氧搅拌,产生大量泡沫;泥龄偏长,污泥老化,也易产生泡沫。
用表面喷淋水或除沫剂去除泡沫,常用除沫剂有机油、煤油、硅油,投量为0.5~1.5mg/L。
通过增加曝气池污泥浓度或适当减小曝气量,也能有效控制泡沫产生。
当废水中含表面活性物质较多时,易预先用泡沫分离法或其他方法去除。
另外也可考虑增设一套除油装置。
但最重要的是要加强水源管理,减少含油过高废水及其它有毒废水的进入3.污泥上浮问题当废水中含油量过大,整个系统泥质变轻,在操作过程中不能很好控制其在二沉池的停留时间,易造成缺氧,产生腐化污泥上浮;当曝气时间过长,在池中发生高度硝化作用,使硝酸盐浓度高,在二沉池易发生反硝化作用,产生氮气,使污泥上浮;另外,废水中含油量过大,污泥可能挟油上浮。