(CMA)
(CNAS)
(ISO)
(高新技术企业)
生物反应器相关标准参考信息
GB/T 42281-2022 膜曝气生物膜反应器（MABR）中空纤维膜组件
简介：
信息：ICS：13.060 CCS：Q81 发布：2022-12-30 实施：2023-07-01
T/CECS 152-2017 膜生物反应器城镇污水处理工艺设计规程
简介：本规程适用于采用微滤或超滤膜生物反应器进行城镇污水处理的新建、扩建和改建工程的设计。
信息：ICS： CCS： 发布：2017-08-22 实施：2017-11-01
ASTM E2871-2012 采用单管法评价铜绿假单胞菌生物膜在疾控中心生物膜反应器中生长的消毒剂疗效的标准试验方法
简介：Vegetative biofilm bacteria are phenotypically different from suspended planktonic cells of the same genotype. Biofilm growth reactors are engineered to produce biofilms with specific characteristics (2). Altering either the engineered system or operating conditions will modify those characteristics as well as the physicochemical environment. The goal in biofilm research and efficacy testing is to choose the growth reactor and operating conditions that generate the most relevant biofilm for the particular study. The test method was developed using Pseudomonas aeruginosa ATCC 15442 biofilm grown on borosilicate glass coupons in the CDC Biofilm Reactor and liquid disinfectants. Efficacy data developed using other bacteria, different shear, different coupons, or other standardized biofilm reactor systems, and/or other forms of disinfectants may result in different log10 reduction (LR) values and repeatability and reproducibility standard deviations. The efficacy test was designed to determine the log10 reduction in bacteria after exposure to a disinfectant in a closed system. The test method was developed using 50-mL conical tubes. The conical geometry allows for disinfectant exposure to biofilm on all surfaces of the coupon. Each efficacy test includes a single contact time and temperature for three untreated control coupons (exposed to buffered dilution water) and three treated coupons (per disinfectant/concentration combination).1.1 This test method specifies the operational parameters required to perform a quantitative liquid disinfectant efficacy test against biofilm bacteria. 1.2 The test method was developed using a Pseudomonas aeruginosa biofilm grown in the CDC Biofilm Reactor (Test Method E2562), modified to include borosilicate glass coupons as a hard nonporous surface and P. aeruginosa ATCC 15442. 1.3 Disinfectant preparation and contact time are used in the assessment according to the manufacturerx2019;s instructions for use. 1.4 The test method uses a closed system to treat biofilm. A coupon is placed in a single tube for the treatment, neutralization, and sampling steps to prevent the loss of cells. 1.5 Verification of disinfectant neutralization is determined prior to conducting the test method. 1.6 This test method describes how to sample and analyze treated and untreated control biofilms for viable cells. Biofilm population density is recorded as log10 colony-forming units per coupon. Efficacy is reported as a log10 reduction of viable cells. 1.7 Basic microbiology training is required to perform this assay. 1.8 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.9 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：71.100.35 (Chemicals for industrial and domestic d CCS： 发布：2012 实施：
GB/T 33898-2017 膜生物反应器通用技术规范
简介：
信息：ICS：07.100.20 CCS：J77 发布：2017-07-12 00:00:00.0 实施：2018-02-01 00:00:00.0
JT/T 1147.1-2017 公路服务区污水处理设施技术要求 第1部分:膜生物反应器处理系统
简介：JT/T 1147的本部分规定了公路服务区污水处理设施膜生物反应器处理系统的处理水量和水质、系统构成和平面布置、处理工艺、检测与控制、日常运行和维护管理。本部分适用于以膜生物反应器为主要处理工艺的公路服务区污水处理设施。采用以膜生物反应器为主要处理工艺的公路其他附属设施污水处理设施可参照使用。
信息：ICS：03.220.20;13.020 CCS：R04 发布：2017-07-04 实施：2017-11-01
ASTM E2562-2012 使用高剪切和连续流量的CDC生物膜反应器量化铜绿假单胞菌生物膜生长的标准试验方法
简介：Bacteria that exist in biofilms are phenotypically different from suspended cells of the same genotype. Research has shown that biofilm bacteria are more difficult to kill than suspended bacteria (5, 7). Laboratory biofilms are engineered in growth reactors designed to produce a specific biofilm type. Altering system parameters will correspondingly result in a change in the biofilm. For example, research has shown that biofilm grown under high shear is more difficult to kill than biofilm grown under low shear (5, 8). The purpose of this test method is to direct a user in the laboratory study of a Pseudomonas aeruginosa biofilm by clearly defining each system parameter. This test method will enable an investigator to grow, sample, and analyze a Pseudomonas aeruginosa biofilm grown under high shear. The biofilm generated in the CDC Biofilm Reactor is also suitable for efficacy testing. After the 48 h growth phase is complete, the user may add the treatment in situ or harvest the coupons and treat them individually.1.1 This test method specifies the operational parameters required to grow a reproducible (1) Pseudomonas aeruginosa biofilm under high shear. The resulting biofilm is representative of generalized situations where biofilm exists under high shear rather than being representative of one particular environment. 1.2 This test method uses the Centers for Disease Control and Prevention (CDC) Biofilm Reactor. The CDC Biofilm Reactor is a continuously stirred tank reactor (CSTR) with high wall shear. Although it was originally designed to model a potable water system for the evaluation of Legionella pneumophila (2), the reactor is versatile and may also be used for growing and/or characterizing biofilm of varying species (3-5). 1.3 This test method describes how to sample and analyze biofilm for viable cells. Biofilm population density is recorded as log10 colony forming units per surface area. 1.4 Basic microbiology training is required to perform this test method. 1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：07.100.01 (Microbiology in general) CCS： 发布：2012 实施：
T/ZGM 014-2022 中空纤维膜生物反应器组器节能产品认证技术要求
简介：规定了中空纤维膜生物反应器组器的节能评价技术内容，主要有：基本要求明确了中空纤维膜组器的性能与节能要求，规范了膜组器在应用过程中的能耗计算方法及相应的能效等级。
信息：ICS：21.020 CCS：N772 发布：2022-11-02 实施：2022-11-02
ASTM E2196-17 用旋转圆盘反应器在中等剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2017-04-01 实施：
ASTM E2196-2012 用旋转盘式反应器量化随剪切连续流生长的铜绿假单胞菌(Pseudomonas aeruginosa)生物膜的标准试验方法
简介：Bacteria that exist in a biofilm are phenotypically different from suspended cells of the same genotype. The study of biofilm in the laboratory requires protocols that account for this difference. Laboratory biofilms are engineered in growth reactors designed to produce a specific biofilm type. Altering system parameters will correspondingly result in a change in the biofilm. The purpose of this method is to direct a user in the laboratory study of biofilms by clearly defining each system parameter. This method will enable a person to grow, sample, and analyze a laboratory biofilm.1.1 This test method is used for growing a reproducible (1) Pseudomonas aeruginosa biofilm in a continuously stirred tank reactor (CSTR) under medium shear conditions. In addition, the test method describes how to sample and analyze biofilm for viable cells. 1.2 Although this test method was created to mimic conditions within a toilet bowl, it can be adapted for the growth and characterization of varying species of biofilm (rotating disk reactorrepeatability and relevance (2)). 1.3 This test method describes how to sample and analyze biofilm for viable cells. Biofilm population density is recorded as log10 colony forming units per surface area (rotating disk reactorefficacy test method (3)). 1.4 Basic microbiology training is required to perform this test method. 1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：07.100.01 (Microbiology in general) CCS： 发布：2012 实施：
T/ZGM 013-2022 平板膜生物反应器组器节能产品认证技术要求
简介：主要技术内容：适用范围、规范性引用文件、术语和定义、技术要求和测试方法等。
信息：ICS：21.020 CCS：N772 发布：2022-11-02 实施：2022-11-02
ASTM E2562-17 使用CDC生物膜反应器在高剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2017-04-01 实施：
ASTM D7475-11 加速生物反应器填埋条件下塑料材料有氧降解和厌氧生物降解的标准测试方法
简介：
信息：ICS：13.030.40 CCS： 发布：2011-01-01 实施：
ASTM E2562-22 用CDC生物膜反应器在高剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2022-05-01 实施：
T/CAQI 19-2016 废水生物增强处理 上流式一体化生物反应器系统工程技术规范
简介：容积负荷：厌氧区（或水解区）为4~8kgCODCr/(m3·d)；好氧区为0.3~0.8kgCODCr/(m3·d)。水力停留时间：厌氧-好氧一体化生物反应器小于48h；水解-好氧一体化生物反应器小于24h。此外，上流式一体化生物反应器水流上升流速应小于1m/h。上流式一体化生物反应器宜采用多点布水装置。布水装置宜采用一管多孔式布水，进水点距反应器底部宜保持150~250mm的距离，等等。
信息：ICS：13.060.30 CCS：N7721 发布：2016-12-22 实施：2017-02-10
ASTM D7475-2011 加速生物反应器填埋场条件下测定塑料材料的耗氧降解和厌氧生物降解的标准试验方法
简介：Decomposition of a plastic within a landfill involves processes in aerobic and anaerobic environmental conditions that can affect the decomposition of other materials enclosed by or in close proximity to the plastic. The rate of change from aerobic to anaerobic conditions is probably a characteristic of the particular landfill site, its garbage and the filling technique and is therefore difficult to assess with any degree of accuracy. Different sources indicate days to months (Refs (8) and (9)) for this change with the spread dependent on the perspective of what is aerobic or anaerobic and how fast the environment changes, 30 days is chosen in this method as a compromise time period. (Note, even very low levels of oxygen, far below normal atmospheric concentration can promote oxidative degradation). Obviously, there will be pockets of protected (in bags, cans, etc.) aerobic activity enclosed in any landfill. There is currently no evidence or data to support claims that rapid degradation of the plastic (when compared to conventional non-degradable plastic) can increase the economic feasibility of landfill-gas recovery, minimize the duration of after-care of the landfill, and make possible the recovery of the volume reduction of the waste due to degradation and biodegradation during the active life of the landfill. Additionally, it is possible that the rapid degradation and biodegradation of plastics can create hazardous conditions in landfills, such as the shifting of cells and overall stability. This standard method has been developed to permit determination of the aerobic degradation and anaerobic biodegradation of plastic products when placed in biologically active environments simulating some landfill conditions. The decomposition of plastic materials in a landfill is of importance, as most landfills are biologically active and are an increasingly significant source of renewable energy. As degradation occurs in a landfill, it is of immediate concern that the plastic materials do not produce toxic metabolites or end products under the various conditions that occur in a landfill. The mixtures remaining after completion of the test method, containing fully or partially degraded plastic materials or extracts can be, when appropriate, submitted subsequently to ecotoxicity testing, see Practice D5951 and Guide D6954 for details, in order to assess the environmental hazards posed by the breakdown of plastics to varying degrees in landfills, especially if leaching occurs. This test method has been designed to assess aerobic degradation and anaerobic biodegradation under optimum and less-than-optimum conditions and toxicity. Limitations8212;Because a wide variation exists in the construction and operation of landfills, and because regulatory requirements for landfills vary greatly, this procedure is not intended to simulate the environments of all landfills. However, it is expected to closely resemble the environment of a biologically active landfill. More specifically, the procedure is intended to create a standard laboratory environment that permits rapid and reproducible determination of the aerobic degradability and anaerobic biodegradability under accelerated landfill conditions, while at the same time producing reproducible mixtures of fully and partially decomposed household waste with plastic materials for ecotoxicological assessment.1.1 This modification of Test Method D5526, which only considered anaerobic degradation, is used to determine the degree and rate of aerobic degradation (as indicated by loss of ten......
信息：ICS：13.030.40 CCS：G31 发布：2011 实施：
ASTM E2196-22 用旋转圆盘反应器在中等剪切和连续流动条件下生长的铜绿假单胞菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2022-05-01 实施：
T/CAQI 21-2016 废水生物增强处理 上流式一体化生物反应器
简介：容积负荷：厌氧区（或水解区）为4~8kgCODCr/(m3·d)；好氧区为0.3~0.8kgCODCr/(m3·d)。水力停留时间：厌氧-好氧一体化生物反应器小于48h；水解-好氧一体化生物反应器小于24h。此外，上流式一体化生物反应器下部厌氧区（或水解区）宜采用生物绳填料，填料填充比为25~40%；上部好氧区宜采用悬浮填料，填料填充比为30~50%，等等。
信息：ICS：13.060.30 CCS：N7721 发布：2016-12-22 实施：2017-05-09
BS CWA 15897-2008 水中膜生物反应器(MBR)技术
简介：
信息：ICS：13.060.30 CCS：J88 发布：2008-11-01 实施：2008-11-01
ASTM E2871-21 用单管法测定CDC生物膜反应器中生物膜消毒剂效力的标准试验方法
简介：
信息：ICS：71.100.35 CCS： 发布：2021-11-01 实施：
DB44/T 1658-2015 水处理用膜生物反应器和紫外线消毒设备
简介：本标准规定了生活污水处理膜生物反应器和封闭式紫外线消毒设备的术语和定义、分类与型号、技术要求、试验方法、检验规则、标志、包装、运输和贮存等要求。 本标准适用于对经过化粪池及格栅预处理后的生活污水进行处理的膜生物反应器与紫外线消毒设备。 原水水质与生活污水相类似的膜生物反应器和紫外线消毒设备可参照执行。
信息：ICS：71.120.99 CCS：G94 发布：2015-09-07 实施：2015-11-07
ASTM E2647-08 使用低剪切和连续流量滴流生物膜反应器生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：13.060.30 CCS： 发布：2008-10-01 实施：
ASTM E3161-21 使用CDC生物膜反应器制备绿脓杆菌或金黄色葡萄球菌生物膜的标准实施规程
简介：
信息：ICS：07.100.01 CCS： 发布：2021-11-01 实施：
HY/T 168.3-2013 大生活用海水后处理设计规范 第3部分:膜生物反应器法
简介：HY/T 168的本部分规定了膜生物反应器法处理含大生活用海水污水系统中的术语、一般规定要求、处理工艺及设施、系统维护、检测监测与控制等内容。本部分适用于膜生物反应器法处理含大生活用海水污水处理工程的设计。
信息：ICS：07.060;13.060.30 CCS：P41 发布：2013-11-13 实施：2014-05-01
ASTM E2647-2008 用低剪切和连续流的滴灌流生物膜反应器量化铜绿假单胞菌(Pseudomonas aeruginosa)生物膜生长的标准试验方法
简介：Vegetative biofilm bacteria are phenotypically different from suspended cells of the same genotype. Biofilm growth reactors are engineered to produce biofilms with specific characteristics. Altering either the engineered system or operating conditions will modify those characteristics. The purpose of this test method is to direct a user in how to grow, sample and analyze a Pseudomonas aeruginosa biofilm under low fluid shear and close to the air/liquid interface using the drip flow reactor. The Pseudomonas aeruginosa biofilm that grows has a smooth appearance and is loosely attached. Microscopically, the biofilm is sheet-like with few architectural details. This laboratory biofilm could represent those found on produce sprayers, on food processing conveyor belts, on catheters, in lungs with cystic fibrosis and oral biofilms, for example. The biofilm generated in the drip flow reactor is also suitable for efficacy testing. After the 54 h growth phase is complete, the user may add the treatment in situ or harvest the coupons and treat them individually. Research has shown that P. aeruginosa biofilms grown in the drip flow reactor were less resistant to disinfection than biofilms grown under high shear conditions. 1.1 This test method specifies the operational parameters required to grow a repeatable Pseudomonas aeruginosa biofilm close to the air/liquid interface in a reactor with a continuous flow of nutrients under low fluid shear conditions. The resulting biofilm is representative of generalized situations where biofilm exists at the air/liquid interface under low fluid shear rather than representative of one particular environment. 1.2 This test method uses the drip flow biofilm reactor. The drip flow reactor (DFR) is a plug flow reactor with laminar flow resulting in low fluid shear. The reactor is versatile and may also be used for growing and/or characterizing different species of biofilms. 1.3 This test method describes how to sample and analyze biofilm for viable cells. Biofilm population density is recorded as log colony forming units per surface area. 1.4 Basic microbiology training is required to perform this test method. 1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：13.060.30;91.010.20 (Contractual aspects) CCS：J88 发布：2008 实施：
T/ZGM 004-2021 “领跑者”标准评价要求 膜生物反应器组器
简介：对制造组器企业标准的评价指标体系与评价方法，确定基础指标、核心指标内容。
信息：ICS：21-010 CCS：C359 发布：2021-10-12 实施：2021-10-15
ASTM E2871-13 用单管法评价CDC生物膜反应器中生长的铜绿假单胞菌生物膜消毒剂效果的标准试验方法
简介：
信息：ICS：71.100.35 CCS： 发布：2013-10-01 实施：
ASTM E2196-07 用旋转圆盘反应器在剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2007-04-01 实施：
T/HW 00018-2020 生活垃圾渗沥液内置式膜生物反应器膜系统技术规定
简介：本标准的主要技术内容是：1.总则；2.术语；3.基本规定；4.内置式膜生物反应器膜系统设计；5.安装、调试与验收；6.运行与维护。
信息：ICS：13.030.01 CCS：N772 发布：2020-07-13 实施：2021-01-22
ASTM E2647-13 用低剪切和连续流动滴流生物膜反应器生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：13.060.30 CCS： 发布：2013-04-01 实施：
ASTM E2562-07 用CDC生物膜反应器在高剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2007-04-01 实施：
ASTM E2647-20 用低剪切和连续流动的滴流式生物膜反应器生长的铜绿假单胞菌生物膜定量的标准试验方法
简介：
信息：ICS：13.060.30 CCS： 发布：2020-04-01 实施：
ASTM E2871-2013 用单管法评估CDC生物膜反应器中生长的绿脓假单胞菌生物膜杀菌有效性的标准试验方法
简介：5.1x00a0;Vegetative biofilm bacteria are phenotypically different from suspended planktonic cells of the same genotype. Biofilm growth reactors are engineered to produce biofilms with specific characteristics (2). Altering either the engineered system or operating conditions will modify those characteristics as well as the physicochemical environment. The goal in biofilm research and efficacy testing is to choose the growth reactor and operating conditions that generate the most relevant biofilm for the particular study. 5.2x00a0;The test method was developed using Pseudomonas aeruginosa ATCC 15442 biofilm grown on borosilicate glass coupons in the CDC Biofilm Reactor and liquid disinfectants. Efficacy data developed using other bacteria, different shear, different coupons, or other standardized biofilm reactor systems, and/or other forms of disinfectants may result in different log10 reduction (LR) values and repeatability and reproducibility standard deviations. 5.3x00a0;The efficacy test was designed to determine the log10 reduction in bacteria after exposure to a disinfectant in a closed system. 5.4x00a0;The test method was developed using 50-mL conical tubes. The conical geometry allows for disinfectant exposure to biofilm on all surfaces of the coupon. 5.5x00a0;Each efficacy test includes a single contact time and temperature for three untreated control coupons (exposed to buffered dilution water) and three treated coupons (per disinfectant/concentration combination). 1.1x00a0;This test method specifies the operational parameters required to perform a quantitative liquid disinfectant efficacy test against biofilm bacteria. 1.2x00a0;The test method was developed using a Pseudomonas aeruginosa biofilm grown in the CDC Biofilm Reactor (Test Method E2562), modified to include borosilicate glass coupons as a hard nonporous surface and P. aeruginosa ATCC 15442. 1.3x00a0;Disinfectant preparation and contact time are used in the assessment according to the manufacturerx2019;s instructions for use. 1.4x00a0;The test method uses a closed system to treat biofilm. A coupon is placed in a single tube for the treatment, neutralization, and sampling steps to prevent the loss of cells. 1.5x00a0;Verification of disinfectant neutralization is determined prior to conducting the test method. 1.6x00a0;This test method describes how to sample and analyze treated and untreated control biofilms for viable cells. Biofilm population density is recorded as log10 colony-forming units per coupon. Efficacy is reported as a log10 reduction of viable cells. 1.7x00a0;Basic microbiology training is required to perform this assay. 1.8x00a0;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1......
信息：ICS：71.100.35 (Chemicals for industrial and domestic d CCS： 发布：2013 实施：
ASTM E2196-2007 用旋转盘式反应器量化随剪切连续流生长的铜绿假单胞菌生物膜的标准试验方法
简介：Bacteria that exist in a biofilm are phenotypically different from suspended cells of the same genotype. The study of biofilm in the laboratory requires protocols that account for this difference. Laboratory biofilms are engineered in growth reactors designed to produce a specific biofilm type. Altering system parameters will correspondingly result in a change in the biofilm. The purpose of this method is to direct a user in the laboratory study of biofilms by clearly defining each system parameter. This method will enable a person to grow, sample, and analyze a laboratory biofilm.1.1 This test method is used for growing a repeatable Pseudomonas aeruginosa biofilm in a continuously stirred flow reactor. In addition, the test method describes how to sample and analyze biofilm for viable cells.1.2 In this test method, biofilm population density is recorded as log colony forming units per surface area.1.3 Basic microbiology training is required to perform this test method. This standard does not claim to address all of the safety problems associated with its use. It is the responsibility of the user of this standard to establish appropriate safety practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：07.100.01 (Microbiology in general) CCS：G92 发布：2007 实施：
T/ZZB 0937-2019 一次性生物反应器
简介：本标准规定了一次性生物反应器的术语和定义、基本要求、分类与标记、技术要求、试验方法、检验规则、标志、使用说明书、包装、运输和贮存、质量承诺及处置要求。本标准适用于非鼓泡传氧（激流式）一次性生物反应器。
信息：ICS：11.120.99 CCS：C271 发布：2019-01-11 实施：2019-03-15
ANSI/AWWA B130-2013 膜生物反应器
简介：
信息：ICS：13.060.30 CCS：J88 发布：2013 实施：
ASTM E2562-2007 用疾病控制中心(CDC)生物膜反应器量化随高剪切连续流动生长的铜绿假单胞菌生物膜的标准试验方法
简介：Bacteria that exist in biofilm are phenotypically different from suspended cells of the same genotype. Research has shown that biofilm bacteria are more difficult to kill than suspended bacteria (5). Laboratory biofilms are engineered in growth reactors designed to produce a specific biofilm type. Altering system parameters will correspondingly result in a change in the biofilm. For example, research has shown that biofilm grown under high shear is more difficult to kill than biofilm grown under low shear (6). The purpose of this test method is to direct a user in the laboratory study of a Pseudomonas aeruginosa biofilm by clearly defining each system parameter. This test method will enable an investigator to grow, sample, and analyze a Pseudomonas aeruginosa biofilm grown under high shear. The biofilm generated in the CDC biofilm reactor is also suitable for efficacy testing. After the 48 h growth phase is complete, the user may add the treatment in situ or harvest the coupons and treat them individually.1.1 This test method specifies the operational parameters required to grow a repeatable Pseudomonas aeruginosa biofilm under high shear (1). The resulting biofilm is representative of generalized situations where biofilm exists under high shear rather than representative of one particular environment.1.2 This test method uses the Centers for Disease Control and Prevention (CDC) biofilm reactor. The CDC biofilm reactor is a continuously stirred flow reactor with high wall shear. Although it was originally designed to model a potable water system for the evaluation of Legionella pneumophila (2), the reactor is versatile and may also be used for growing and/or characterizing biofilm of varying species (3 and 4).1.3 This test method describes how to sample and analyze biofilm for viable cells. Biofilm population density is recorded as log colony forming units per surface area.1.4 Basic microbiology training is required to perform this test method. 1.5 The values stated in SI units are to be regarded as the standard. The values given in parentheses are for information only.1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：07.100.01 (Microbiology in general) CCS：C04 发布：2007 实施：
ASTM E2871-19 用单管法测定CDC生物膜反应器中生物膜消毒剂效力的标准试验方法
简介：
信息：ICS：71.100.35 CCS： 发布：2019-01-01 实施：
ASTM E2647-2013 使用低剪切和连续流量的滴流生物膜反应器量化铜绿假单胞菌生物膜生长的标准试验方法
简介：5.1x00a0;Vegetative biofilm bacteria are phenotypically different from suspended cells of the same genotype. Biofilm growth reactors are engineered to produce biofilms with specific characteristics. Altering either the engineered system or operating conditions will modify those characteristics. 5.2x00a0;The purpose of this test method is to direct a user in how to grow, sample, and analyze a P. aeruginosa biofilm under low fluid shear and close to the air/liquid interface using the DFR. The P. aeruginosa biofilm that grows has a smooth appearance and is loosely attached. Microscopically, the biofilm is sheet-like with few architectural details. This laboratory biofilm could represent those found on produce sprayers, on food processing conveyor belts, on catheters, in lungs with cystic fibrosis, and oral biofilms, for example. The biofilm generated in the DFR is also suitable for efficacy testing. After the 54 h growth phase is complete, the user may add the treatment in8201;situ or harvest the coupons and treat them individually. Research has shown that P. aeruginosa biofilms grown in the DFR were less tolerant to disinfection than biofilms grown under high shear conditions.5 1.1x00a0;This test method specifies the operational parameters required to grow a repeatable2 Pseudomonas aeruginosa biofilm close to the air/liquid interface in a reactor with a continuous flow of nutrients under low fluid shear conditions. The resulting biofilm is representative of generalized situations where biofilm exists at the air/liquid interface under low fluid shear rather than representative of one particular environment. 1.2x00a0;This test method uses the drip flow reactor. The drip flow reactor (DFR) is a plug flow reactor with laminar flow resulting in low fluid shear. The reactor is versatile and may also be used for growing and/or characterizing biofilms of different species, although this will require changing the operational parameters to optimize the method based upon the growth requirements of the new organism. 1.3x00a0;This test method describes how to sample and analyze biofilm for viable cells. Biofilm population density is recorded as log colony forming units per surface area. 1.4x00a0;Basic microbiology training is required to perform this test method. 1.5x00a0;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.6x00a0;This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：13.060.30 (Sewage water) CCS： 发布：2013 实施：
HG/T 3917-2006 污水处理膜 生物反应器装置
简介：本标准规定了污水处理膜-生物反应器装置的名词术语、产品分类、技术要求，以及检验、包装和贮运等要求。 本标准适用于处理医疗机构污水的一体式膜-生物反应器装置 , 对于处理其他污水的一体式膜-生物反应器，或者处理医疗机构污水的分置式膜-生物反应器，也可参照执行。
信息：ICS：71.120.99 CCS：G94 发布：2006-07-26 实施：2007-03-01
T/CAQI 59-2018 污（废）水生物处理 移动床生物膜反应器系统工程技术规范
简介：
信息：ICS：13.060.30 CCS：G90/99 发布：2018-12-26 实施：2019-01-01
HJ 2528-2012 环境保护产品技术要求 中空纤维膜生物反应器组器
简介：
信息：ICS：01.040.13 CCS：z 发布：2012-07-31 实施：2012-11-01
CECS 152-2003 一体式膜生物反应器污水处理应用技术规程
简介：本规程适用于以中空纤维膜组件构成的内置式膜生物反应器处理污水和污水回用的设备设计、安装、应用及运行管理。对采用平板式膜组件和管式膜组件构成的反应器，也可参照执行。
信息：ICS：13.060.30 CCS：P41 发布：2003-08-12 实施：2003-10-01
T/CAQI 61-2018 污（废）水生物处理 好氧循环生物膨胀床反应器
简介：
信息：ICS：13.060.30 CCS：J88 发布：2018-12-26 实施：2019-01-01
HJ 2527-2012 环境保护产品技术要求.膜生物反应器
简介：本标准规定了膜生物反应器的定义、分类与命名、基本要求、性能要求、试验方法、检验规则及标志、包装、运输和贮存。本标准适用于日处理水量不大于500m³/d生活污水和可生化处理的工业废水处理或回用的膜生物反应器。
信息：ICS： CCS：J88 发布：2012-07-31 实施：2012-11-01
CECS 152-2003（条文说明） 一体式膜生物反应器污水处理应用技术规程
简介：
信息：ICS：13.060.30 CCS：P41 发布：2003-08-12 实施：2003-10-01
T/CAQI 61-2018 污（废）水生物处理 好氧循环生物膨胀床反应器
简介：反应器组成、工艺流程、结构要求、制造要求、性能要求
信息：ICS：13.060.30 CCS：D4620 发布：2018-12-26 实施：2019-02-01
HJ 2528-2012 环境保护产品技术要求.中空纤维膜生物反应器组器
简介：本标准规定了中空纤维膜生物反应器组器的定义、分类与命名、技术要求、检验方法、检验规则及标志、包装运输和贮存。本标准适用于浸没式膜生物反应器处理生活污水和处理可生化工业废水的工艺。
信息：ICS： CCS：J88 发布：2012-07-31 实施：2012-11-01
ASTM E2196-02 用旋转圆盘反应器在剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2002-04-10 实施：
T/CAQI 60-2018 污（废）水生物处理 高负荷内循环厌氧反应器
简介：
信息：ICS：13.060.30 CCS：Z00/09 发布：2018-12-26 实施：2019-01-01
HJ 2527-2012 环境保护产品技术要求 膜生物反应器
简介：
信息：ICS：01.040.13 CCS：z 发布：2012-07-31 实施：2012-11-01
BS EN 12255-7-2002 污水处理厂.生物固定薄膜反应器
简介：This European Standard specifies the design principles and performance requirements for secondary treatment by biological fixed-film reactors at wastewater treatment plants for more than 50 PT.The primary application is for wastewater treatment plants designed for the treatment of domestic and municipal wastewater.Biological fixed film reactors include biological trickling filters, rotating biological contactors, submerged bed reactors and biofilters.Differences in wastewater treatment throughout Europe have led to a variety of systems being developed. This standard gives fundamental informations about the systems; this standard has not attempted to specify all available systems.Detailed information additional to that contained in this standard may be obtained by referring to the Bibliography.
信息：ICS：13.060.30 CCS：P41 发布：2002-04-05 实施：2002-04-05
T/CAQI 60-2018 污（废）水生物处理 高负荷内循环厌氧反应器
简介：基础要求、设计要求、制造要求、性能要求、安全要求。
信息：ICS：13.060.30 CCS：D4620 发布：2018-12-26 实施：2019-02-01
ASTM E2871-12 用单管法评估CDC生物膜反应器中生长的绿脓杆菌的消毒效果的标准试验方法
简介：
信息：ICS：71.100.35 CCS： 发布：2012-04-01 实施：
NF P16-700-7-2002 废水处理厂.第7部分:固定生物膜反应器
简介：
信息：ICS：13.060.30 CCS：Q81 发布：2002-04-01 实施：2002-04-05
T/CAQI 59-2018 污（废）水生物处理 移动床生物膜反应器系统工程技术规范
简介：设计要求：池体结构、填料、水质指标、搅拌设计、曝气设计、拦截筛网（筒）设计。
信息：ICS：13.060.30 CCS：D4620 发布：2018-12-26 实施：2019-02-01
ASTM E2562-12 用CDC生物膜反应器在高剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2012-04-01 实施：
DIN EN 12255-7-2002 污水处理厂.第7部分:生物固定薄膜反应器
简介：This European Standard specifies the design principles and performance requirements for secondary treatment by biological fixed-film reactors at wastewater treatment plants for more than 50 PT. The primary application is for wastewater treatment plants designed for the treatment of domestic and municipal wastewater. Biological fixed film reactors include biological trickling filters, rotating biological contactors, submerged bed reactors and biofilters.
信息：ICS：13.060.30 CCS：J88 发布：2002-04 实施：
ASTM E3161-18 使用CDC生物膜反应器制备绿脓杆菌或金黄色葡萄球菌生物膜的标准实施规程
简介：
信息：ICS：07.100.01 CCS： 发布：2018-04-01 实施：
ASTM E2196-12 用旋转圆盘反应器在介质剪切和连续流动条件下生长的绿脓杆菌生物膜定量的标准试验方法
简介：
信息：ICS：07.100.01 CCS： 发布：2012-04-01 实施：
EN 12255-7-2002 废水处理工厂.第7部分:生物固定膜反应器
简介：This European Standard specifies the design principles and performance requirements for secondary treatment by biological fixed-film reactors at wastewater treatment plants for more than 50 PT.The primary application is for wastewater treatment plants designed forThe treatment of domestic and municipal wastewater.Biological fixed film reactors include biological trickling filters, rotating biological contactors, submerged bed reactors and biofilters.Differences in wastewater treatment throughout Europe have led to a variety of systems being developed.This standard gives fundamental informations aboutThe systems;This standard has not attempted to specify all available systems.Detailed information additional to that contained inThis standard may be obtained by referring toThe Bibliography
信息：ICS：13.060.30 CCS： 发布：2002-01-01 实施：
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