CN116067846A - A method for testing the mechanical strength of aerobic granular sludge - Google Patents
A method for testing the mechanical strength of aerobic granular sludge Download PDFInfo
- Publication number
- CN116067846A CN116067846A CN202211619970.0A CN202211619970A CN116067846A CN 116067846 A CN116067846 A CN 116067846A CN 202211619970 A CN202211619970 A CN 202211619970A CN 116067846 A CN116067846 A CN 116067846A
- Authority
- CN
- China
- Prior art keywords
- granular sludge
- mechanical strength
- aerobic granular
- particle size
- testing
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 80
- 238000012360 testing method Methods 0.000 title claims abstract description 48
- 238000000034 method Methods 0.000 title claims abstract description 27
- 239000002245 particle Substances 0.000 claims abstract description 68
- 230000008859 change Effects 0.000 claims abstract description 64
- 230000009471 action Effects 0.000 claims abstract description 31
- 239000008367 deionised water Substances 0.000 claims description 3
- 229910021641 deionized water Inorganic materials 0.000 claims description 3
- 239000002270 dispersing agent Substances 0.000 claims description 3
- 238000010008 shearing Methods 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical group O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 3
- 238000012512 characterization method Methods 0.000 abstract description 4
- 238000010586 diagram Methods 0.000 abstract description 4
- 238000011002 quantification Methods 0.000 abstract 1
- 238000010998 test method Methods 0.000 description 7
- 239000002028 Biomass Substances 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 3
- 239000008187 granular material Substances 0.000 description 3
- 239000012528 membrane Substances 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 101001121408 Homo sapiens L-amino-acid oxidase Proteins 0.000 description 2
- 102100026388 L-amino-acid oxidase Human genes 0.000 description 2
- 238000002835 absorbance Methods 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000006835 compression Effects 0.000 description 2
- 238000007906 compression Methods 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 230000007246 mechanism Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 230000004044 response Effects 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- CZMRCDWAGMRECN-UGDNZRGBSA-N Sucrose Chemical compound O[C@H]1[C@H](O)[C@@H](CO)O[C@@]1(CO)O[C@@H]1[C@H](O)[C@@H](O)[C@H](O)[C@@H](CO)O1 CZMRCDWAGMRECN-UGDNZRGBSA-N 0.000 description 1
- 229930006000 Sucrose Natural products 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 229910001424 calcium ion Inorganic materials 0.000 description 1
- 230000009089 cytolysis Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000002207 metabolite Substances 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000012163 sequencing technique Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000005720 sucrose Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
Images
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N15/00—Investigating characteristics of particles; Investigating permeability, pore-volume or surface-area of porous materials
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N15/00—Investigating characteristics of particles; Investigating permeability, pore-volume or surface-area of porous materials
- G01N15/02—Investigating particle size or size distribution
- G01N15/0205—Investigating particle size or size distribution by optical means
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Chemical & Material Sciences (AREA)
- Dispersion Chemistry (AREA)
- Physics & Mathematics (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Treatment Of Sludge (AREA)
- Activated Sludge Processes (AREA)
Abstract
本发明公开一种测试好氧颗粒污泥机械强度的方法,包括以下步骤:采用激光粒度分析仪在不同转速下剪切好氧颗粒污泥样品,通过Dv10/50/90随作用时间变化图去除偏差较大的点;绘制在等间隔作用时间下的粒径分布变化图;利用软件分析并提取峰面积等的变化率
或变化量△S信息,绘制出以作用时间为横坐标,或△S为纵坐标的散点图,拟合曲线,通过曲线量化表征其机械强度。其中,峰面积变化率(或变化量)越小,说明好氧颗粒污泥的机械强度越好。本发明可实现简便、精确的好氧颗粒污泥机械强度的量化表征及其标准化测试,形成标准化的数据体系,有利于不同反应器培养形成的好氧颗粒污泥机械强度的比较,为进一步提高反应器的稳定运行提供有益参考。The invention discloses a method for testing the mechanical strength of aerobic granular sludge, comprising the following steps: using a laser particle size analyzer to cut aerobic granular sludge samples at different rotating speeds, and removing the Points with large deviation; draw the particle size distribution change graph under equal interval action time; use software to analyze and extract the change rate of peak area, etc.
Or change △S information, draw the action time as the abscissa, Or △S is the scatter diagram of the ordinate, fitting the curve, and characterizing its mechanical strength through curve quantification. Among them, the smaller the change rate (or change amount) of the peak area, the better the mechanical strength of the aerobic granular sludge. The present invention can realize simple and accurate quantitative characterization and standardized test of the mechanical strength of aerobic granular sludge, form a standardized data system, and facilitate the comparison of the mechanical strength of aerobic granular sludge formed in different reactors, in order to further improve The stable operation of the reactor provides a useful reference.Description
技术领域Technical Field
本发明属于废水生物处理技术领域,更具体地,涉及一种测试好氧颗粒污泥机械强度的方法。The invention belongs to the technical field of wastewater biological treatment, and more specifically, relates to a method for testing the mechanical strength of aerobic granular sludge.
背景技术Background Art
好氧颗粒污泥(Aerobic Granular Sludge,AGS)是一种在好氧条件下通过微生物自凝聚作用形成的颗粒状活性污泥。相比传统的活性污泥法,AGS技术具有高生物量积累、沉降性能好、抗污染负荷冲击的能力、占地面积小等特点。Aerobic Granular Sludge (AGS) is a granular activated sludge formed by microbial self-agglomeration under aerobic conditions. Compared with the traditional activated sludge method, AGS technology has the characteristics of high biomass accumulation, good sedimentation performance, ability to resist pollution load shock, and small footprint.
迄今为止,好氧颗粒污泥生物反应器包括了膜生物反应器(MBR)和序批式反应器(SBR)等。但这些生物反应器设计的成功与否与其形成致密颗粒、保持高生物量的能力有关。颗粒聚集体中紧密的细胞堆积优化了代谢物的种间交换,从而提高整体活性。To date, aerobic granular sludge bioreactors include membrane bioreactors (MBRs) and sequencing batch reactors (SBRs). However, the success of these bioreactor designs is related to their ability to form dense granules and maintain high biomass. The tight cell packing in granular aggregates optimizes the interspecies exchange of metabolites, thereby improving overall activity.
然而,从反应器运行情况上看,过高/低有机负荷率(OLR)和过高的水力学条件等对颗粒造成负面影响,可能导致裂解和分散,生物量显著减少,最终导致系统恶化甚至失效。从运行时间上看,长时间运行后AGS易解体。因此,维持AGS的稳定性是反应器稳定运行的关键,而其机械性能则是表征其稳定性的重要指标。总体而言,AGS的机械性能分为抗压性能和抗剪切性能。现有的抗压性能测试方法如中国专利CN 104062224 A所公开的一种颗粒污泥弹性模量的测量装置及其测量方法。抗剪切性能的测试方法包括完整性系数法(采用振动筛,通过测量上清液中固体质量与好氧颗粒污泥总重的比值来评判)、失稳系数法(采用超声仪,等间隔时间收集的样品在600nm波长下进行吸光度值测试,拟合曲线的斜率即为失稳系数)等。可见,现有测试方法具有快速测量的优点,但测试中需将收集的样品及时倒回,以防止体积变化对实验结果造成影响,因此,建立一种同时满足简便、精确测定其机械强度的方法尤为重要。However, from the perspective of reactor operation, excessively high/low organic loading rate (OLR) and excessively high hydraulic conditions have a negative impact on the particles, which may lead to lysis and dispersion, a significant reduction in biomass, and ultimately lead to system deterioration or even failure. From the perspective of operating time, AGS is prone to disintegration after long-term operation. Therefore, maintaining the stability of AGS is the key to the stable operation of the reactor, and its mechanical properties are an important indicator to characterize its stability. In general, the mechanical properties of AGS are divided into compression resistance and shear resistance. Existing compression resistance test methods such as a measuring device for the elastic modulus of granular sludge and its measuring method disclosed in Chinese patent CN 104062224 A. The test methods for shear resistance include the integrity coefficient method (using a vibrating screen to judge by measuring the ratio of the solid mass in the supernatant to the total weight of aerobic granular sludge), the instability coefficient method (using an ultrasonic instrument, samples collected at equal intervals are tested for absorbance at a wavelength of 600nm, and the slope of the fitting curve is the instability coefficient), etc. It can be seen that the existing test method has the advantage of rapid measurement, but the collected samples need to be returned in time during the test to prevent the volume change from affecting the experimental results. Therefore, it is particularly important to establish a method that can simultaneously meet the requirements of simple and accurate measurement of its mechanical strength.
发明内容Summary of the invention
本发明为克服上述现有技术中的缺陷,提供一种测试好氧颗粒污泥机械强度的方法,可实现简便、精确的好氧颗粒污泥机械强度的量化表征及其标准化测试。In order to overcome the defects in the prior art, the present invention provides a method for testing the mechanical strength of aerobic granular sludge, which can realize simple and accurate quantitative characterization and standardized testing of the mechanical strength of aerobic granular sludge.
为解决上述技术问题,本发明采用的技术方案是:一种测试好氧颗粒污泥机械强度的方法,包括以下步骤:In order to solve the above technical problems, the technical solution adopted by the present invention is: a method for testing the mechanical strength of aerobic granular sludge, comprising the following steps:
S1.采用激光粒度分析仪在不同转速下剪切好氧颗粒污泥样品,通过Dv10/50/90随作用时间变化图去除偏差较大的点;S1. Use laser particle size analyzer to shear aerobic granular sludge samples at different speeds, and remove points with large deviations through the Dv10/50/90 versus action time graph;
S2.绘制在等间隔作用时间t下的粒径分布变化图;S2. Plotting the particle size distribution change at equal intervals of time t;
S3.从步骤S2中利用软件分析并提取峰面积变化率或变化量△S的信息,绘制出以作用时间为横坐标,峰面积变化率或变化量△S为纵坐标的散点图,拟合曲线,通过曲线量化表征好氧颗粒污泥的机械强度;峰面积变化率或变化量越小,表明颗粒在剪切过程中粒径变化较小,则好氧颗粒污泥的机械强度越好。S3. Analyze and extract the peak area change rate from step S2 using software Or the information of the change △S, plot the peak area change rate with the action time as the horizontal axis Or a scatter plot with the change △S as the ordinate, a fitting curve is formed, and the mechanical strength of the aerobic granular sludge is quantitatively characterized by the curve; the smaller the peak area change rate or change amount, the smaller the particle size change during the shear process, and the better the mechanical strength of the aerobic granular sludge.
其中,S为粒径分布与x轴围成的区域面积,即峰面积;t为粒径分布测试的作用时间。Wherein, S is the area enclosed by the particle size distribution and the x-axis, i.e., the peak area; t is the action time of the particle size distribution test.
本发明所提供的测试方法以抗剪切性能表征AGS的机械性能,是通过粒径分布峰面积等变化率或变化量来量化表征好氧颗粒污泥的机械强度,有利于对不同反应器培养形成的好氧颗粒污泥进行机械强度比较,为建立反应器操作要素和颗粒机械强度的响应机制提供依据,也为培养良好强度好氧颗粒污泥提供最优方案具有重要的现实意义和经济价值。The test method provided by the present invention characterizes the mechanical properties of AGS by shear resistance, and quantitatively characterizes the mechanical strength of aerobic granular sludge by the change rate or change amount of particle size distribution peak area, etc., which is conducive to comparing the mechanical strength of aerobic granular sludge formed by cultivation in different reactors, providing a basis for establishing the response mechanism of reactor operating factors and particle mechanical strength, and also providing the optimal solution for cultivating aerobic granular sludge with good strength, which has important practical significance and economic value.
其中,好氧颗粒污泥不限生物反应器培养形成;好氧颗粒污泥的机械强度也可称为抗剪切性能、结构稳定性或机械稳定性。Among them, aerobic granular sludge is not limited to the formation of bioreactor culture; the mechanical strength of aerobic granular sludge can also be called shear resistance, structural stability or mechanical stability.
进一步地,在所述的步骤S3中,还能通过峰高的变化量△h或变化率表征好氧颗粒污泥的机械强度;其中,h为x轴与峰顶点之间的最短距离,即峰高。Furthermore, in step S3, the peak height change Δh or change rate can be used to Characterizes the mechanical strength of aerobic granular sludge; where h is the shortest distance between the x-axis and the peak apex, that is, the peak height.
进一步地,还能通过峰顶点的变化量△d或变化率表征好氧颗粒污泥的机械强度,其中,d为相邻两个峰顶点之间的距离。Furthermore, the peak value change △d or change rate can be Characterizes the mechanical strength of aerobic granular sludge, where d is the distance between two adjacent peak vertices.
进一步地,还能通过极限峰值粒径R表征好氧颗粒污泥的机械强度,其中,R为峰值粒径,此处特别表示极限峰值粒径,是通过Dv10/50/90随作用时间变化图得出。Furthermore, the mechanical strength of aerobic granular sludge can be characterized by the limiting peak particle size R, wherein R is the peak particle size, specifically representing the limiting peak particle size, which is obtained by a graph showing the change of Dv10/50/90 with the action time.
进一步地,在步骤S1中,所选取的好氧颗粒污泥一般为现取样品,先通过筛网去除悬浮絮状污泥,再使用涡旋混合器混合均匀,以确保测试的准确性。Furthermore, in step S1, the selected aerobic granular sludge is generally a freshly taken sample, which is first passed through a sieve to remove suspended flocculent sludge, and then mixed evenly using a vortex mixer to ensure the accuracy of the test.
进一步地,在所述的步骤S2中,横坐标为好氧颗粒污泥的颗粒粒径,纵坐标为容量占比。Furthermore, in the step S2, the abscissa is the particle size of the aerobic granular sludge, and the ordinate is the capacity percentage.
进一步地,所述的步骤S1中,好氧颗粒污泥剪切前的粒径为200μm~3000μm。优选500μm~2500μm。Furthermore, in the step S1, the particle size of the aerobic granular sludge before shearing is 200 μm to 3000 μm, preferably 500 μm to 2500 μm.
进一步地,所述的步骤S1中,转速ω为500r/min-3500r/min。Furthermore, in the step S1, the rotation speed ω is 500r/min-3500r/min.
进一步地,在所述的步骤S1中,作用时间为15min~90min;以1.5min~5min进行等间隔时间测试。优选作用时间为30min~60min;以1.5min~2.5min进行等间隔时间测试。Furthermore, in the step S1, the action time is 15min to 90min, and the test is performed at equal intervals of 1.5min to 5min. Preferably, the action time is 30min to 60min, and the test is performed at equal intervals of 1.5min to 2.5min.
进一步地,在所述的步骤S1中,激光粒度分析仪为Malvern MS3000,参数设置如下:分散剂为去离子水;折射率为1~2;吸收率为0.05~0.2;遮光度为5~50。Furthermore, in the step S1, the laser particle size analyzer is Malvern MS3000, and the parameters are set as follows: the dispersant is deionized water; the refractive index is 1-2; the absorptivity is 0.05-0.2; and the shading degree is 5-50.
进一步地,测试结果需满足Dv10、Dv50、Dv90的RSD值分别<10、6、10,拟合加权<2.5%;其中,Dv10表示10%样品粒径小于该值,Dv50表示50%样品粒径小于该值,Dv90表示90%样品粒径小于该值。Furthermore, the test results must satisfy the RSD values of Dv10, Dv50, and Dv90 of <10, 6, and 10, respectively, and the fitting weighting <2.5%; wherein Dv10 indicates that 10% of the sample particle sizes are smaller than this value, Dv50 indicates that 50% of the sample particle sizes are smaller than this value, and Dv90 indicates that 90% of the sample particle sizes are smaller than this value.
与现有技术相比,有益效果是:Compared with the prior art, the beneficial effects are:
1、本发明采用常用于测量颗粒粒径的仪器——激光粒度分析仪,具有快速、精确、自动化程度高、受浓度和外界因素影响较小等特点。1. The present invention adopts a laser particle size analyzer, which is an instrument commonly used to measure particle size, and has the characteristics of being fast, accurate, highly automated, and less affected by concentration and external factors.
2、本发明测试方法通过峰面积或峰高的变化量/变化率等量化表征好氧颗粒污泥机械强度,在不同转速下对不同生物反应器生成的颗粒进行测试对比,具有普遍性和实用性。本发明可实现简便、精确的好氧颗粒污泥机械强度的量化表征及其标准化测试,形成标准化的数据体系,有利于不同反应器培养形成的好氧颗粒污泥机械强度的比较,为进一步提高反应器的稳定运行提供有益参考。2. The test method of the present invention quantitatively characterizes the mechanical strength of aerobic granular sludge by the change amount/change rate of peak area or peak height, and tests and compares the granules generated by different bioreactors at different rotation speeds, which is universal and practical. The present invention can realize simple and accurate quantitative characterization of the mechanical strength of aerobic granular sludge and its standardized test, forming a standardized data system, which is conducive to the comparison of the mechanical strength of aerobic granular sludge cultivated in different reactors, and provides a useful reference for further improving the stable operation of the reactor.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为本测试好氧颗粒污泥机械强度的方法的流程框图。FIG1 is a flowchart of the method for testing the mechanical strength of aerobic granular sludge.
图2为实施例的在等间隔作用时间下粒径分布变化图。FIG. 2 is a graph showing the change in particle size distribution of an embodiment at equal intervals of action time.
图3为实施例的峰面积变化率随作用时间变化的拟合曲线图。FIG. 3 is a fitting curve diagram showing the peak area change rate versus action time of the embodiment.
具体实施方式DETAILED DESCRIPTION
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明的一部分实施例,而不是全部的实施例。下面结合具体实施方式对本发明作在其中一个实施例中说明。其中,附图仅用于示例性说明,表示的仅是示意图,而非实物图,不能理解为对本专利的限制;为了更好地说明本发明的实施例,附图某些部件会有省略、放大或缩小,并不代表实际产品的尺寸;对本领域技术人员来说,附图中某些公知结构及其说明可能省略是可以理解的。The following will be combined with the drawings in the embodiments of the present invention to clearly and completely describe the technical solutions in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of the embodiments. The present invention is described in one of the embodiments in combination with the specific implementation methods. Among them, the drawings are only used for exemplary descriptions, and only schematic diagrams are shown, not physical drawings, and cannot be understood as limitations on this patent; in order to better illustrate the embodiments of the present invention, some parts of the drawings will be omitted, enlarged or reduced, and do not represent the size of the actual product; for those skilled in the art, it is understandable that some well-known structures and their descriptions in the drawings may be omitted.
在本发明的描述中,需要理解的是,若有术语“上”、“下”、“左”、“右”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此附图中描述位置关系的用语仅用于示例性说明,不能理解为对本专利的限制,对于本领域的普通技术人员而言,可以根据具体情况理解上述术语的具体含义。另外,若本发明实施例中有涉及“第一”、“第二”等的描述,则该“第一”、“第二”等的描述仅用于描述目的,而不能理解为指示或暗示其相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”的特征可以明示或者隐含地包括至少一个该特征。另外,全文中出现的“和/或”的含义为,包括三个并列的方案,以“A和/或B”为例,包括A方案,或B方案,或A和B同时满足的方案。In the description of the present invention, it should be understood that if the terms "upper", "lower", "left", "right" and the like indicate an orientation or positional relationship based on the orientation or positional relationship shown in the drawings, it is only for the convenience of describing the present invention and simplifying the description, rather than indicating or implying that the device or element referred to must have a specific orientation, be constructed and operated in a specific orientation. Therefore, the terms describing the positional relationship in the drawings are only used for exemplary explanations and cannot be understood as limitations on this patent. For ordinary technicians in this field, the specific meanings of the above terms can be understood according to specific circumstances. In addition, if there are descriptions involving "first", "second", etc. in the embodiments of the present invention, the descriptions of "first", "second", etc. are only used for descriptive purposes, and cannot be understood as indicating or implying their relative importance or implicitly indicating the number of technical features indicated. Therefore, the features defined as "first" and "second" can explicitly or implicitly include at least one of the features. In addition, the meaning of "and/or" appearing in the full text is to include three parallel schemes. Taking "A and/or B" as an example, it includes scheme A, or scheme B, or schemes that satisfy both A and B.
实施例1:Embodiment 1:
如图1所示,一种测试好氧颗粒污泥机械强度的方法,包括以下步骤:As shown in FIG1 , a method for testing the mechanical strength of aerobic granular sludge comprises the following steps:
S1.采用激光粒度分析仪在不同转速下剪切好氧颗粒污泥样品,通过Dv10/50/90随作用时间变化图去除偏差较大的点;S1. Use laser particle size analyzer to shear aerobic granular sludge samples at different speeds, and remove points with large deviations through the Dv10/50/90 versus action time graph;
S2.绘制在等间隔作用时间t下的粒径分布变化图;S2. Plotting the particle size distribution change at equal intervals of time t;
S3.从步骤S2中利用软件分析并提取峰面积变化率或变化量△S的信息,绘制出以作用时间为横坐标,峰面积变化率或变化量△S为纵坐标的散点图,拟合曲线,通过曲线量化表征好氧颗粒污泥的机械强度;峰面积变化率或变化量越小,表明颗粒在剪切过程中粒径变化较小,则好氧颗粒污泥的机械强度越好。S3. Analyze and extract the peak area change rate from step S2 using software Or the information of the change △S, plot the peak area change rate with the action time as the horizontal axis Or a scatter plot with the change △S as the ordinate, a fitting curve is formed, and the mechanical strength of the aerobic granular sludge is quantitatively characterized by the curve; the smaller the peak area change rate or change amount, the smaller the particle size change during the shear process, and the better the mechanical strength of the aerobic granular sludge.
其中,S为粒径分布与x轴围成的区域面积,即峰面积;t为粒径分布测试的作用时间。Wherein, S is the area enclosed by the particle size distribution and the x-axis, i.e., the peak area; t is the action time of the particle size distribution test.
本发明所提供的测试方法以抗剪切性能表征AGS的机械性能,是通过粒径分布峰面积等变化率或变化量来量化表征好氧颗粒污泥的机械强度,有利于对不同反应器培养形成的好氧颗粒污泥进行机械强度比较,为建立反应器操作要素和颗粒机械强度的响应机制提供依据,也为培养良好强度好氧颗粒污泥提供最优方案具有重要的现实意义和经济价值。The test method provided by the present invention characterizes the mechanical properties of AGS by shear resistance, and quantitatively characterizes the mechanical strength of aerobic granular sludge by the change rate or change amount of particle size distribution peak area, etc., which is conducive to comparing the mechanical strength of aerobic granular sludge formed by cultivation in different reactors, providing a basis for establishing the response mechanism of reactor operating factors and particle mechanical strength, and also providing the optimal solution for cultivating aerobic granular sludge with good strength, which has important practical significance and economic value.
其中,好氧颗粒污泥不限生物反应器培养形成;好氧颗粒污泥的机械强度也可称为抗剪切性能、结构稳定性或机械稳定性。Among them, aerobic granular sludge is not limited to the formation of bioreactor culture; the mechanical strength of aerobic granular sludge can also be called shear resistance, structural stability or mechanical stability.
其中,在所述的步骤S3中,还能通过峰高的变化量△h或变化率表征好氧颗粒污泥的机械强度;其中,h为x轴与峰顶点之间的最短距离,即峰高。In the step S3, the peak height change Δh or change rate can also be used. Characterizes the mechanical strength of aerobic granular sludge; where h is the shortest distance between the x-axis and the peak apex, that is, the peak height.
另外,还能通过峰顶点的变化量△d或变化率表征好氧颗粒污泥的机械强度,其中,d为相邻两个峰顶点之间的距离。还能通过极限峰值粒径R表征好氧颗粒污泥的机械强度,其中,R为峰值粒径,此处特别表示极限峰值粒径,是通过Dv10/50/90随作用时间变化图得出。In addition, the peak value can be measured by the change in the peak value △d or the rate of change Characterize the mechanical strength of aerobic granular sludge, where d is the distance between two adjacent peak vertices. The mechanical strength of aerobic granular sludge can also be characterized by the limiting peak particle size R, where R is the peak particle size, which specifically refers to the limiting peak particle size, which is obtained by the Dv10/50/90 versus action time graph.
具体的,在步骤S1中,所选取的好氧颗粒污泥一般为现取样品,先通过筛网去除悬浮絮状污泥,再使用涡旋混合器混合均匀,以确保测试的准确性。在所述的步骤S2中,横坐标为好氧颗粒污泥的颗粒粒径,纵坐标为容量占比。Specifically, in step S1, the selected aerobic granular sludge is generally a freshly taken sample, which is first passed through a sieve to remove suspended flocculent sludge, and then mixed evenly using a vortex mixer to ensure the accuracy of the test. In the step S2, the abscissa is the particle size of the aerobic granular sludge, and the ordinate is the volume percentage.
其中,所述的步骤S1中,好氧颗粒污泥剪切前的粒径为200μm~3000μm。优选500μm~2500μm。所述的步骤S1中,转速ω为500r/min-3500r/min。在所述的步骤S1中,作用时间为15min~90min;以1.5min~5min进行等间隔时间测试。优选作用时间为30min~60min;以1.5min~2.5min进行等间隔时间测试。在所述的步骤S1中,激光粒度分析仪为MalvernMS3000,参数设置如下:分散剂为去离子水;折射率为1~2;吸收率为0.05~0.2;遮光度为5~50。Wherein, in the step S1, the particle size of the aerobic granular sludge before shearing is 200μm to 3000μm. Preferably, it is 500μm to 2500μm. In the step S1, the rotation speed ω is 500r/min-3500r/min. In the step S1, the action time is 15min to 90min; and the test is performed at equal intervals of 1.5min to 5min. The preferred action time is 30min to 60min; and the test is performed at equal intervals of 1.5min to 2.5min. In the step S1, the laser particle size analyzer is MalvernMS3000, and the parameters are set as follows: the dispersant is deionized water; the refractive index is 1 to 2; the absorbance is 0.05 to 0.2; and the shading degree is 5 to 50.
具体的,测试结果需满足Dv10、Dv50、Dv90的RSD值分别<10、6、10,拟合加权<2.5%;其中,Dv10表示10%样品粒径小于该值,Dv50表示50%样品粒径小于该值,Dv90表示90%样品粒径小于该值。Specifically, the test results must satisfy the RSD values of Dv10, Dv50, and Dv90 of <10, 6, and 10, respectively, and the fitting weighting <2.5%; wherein Dv10 means that 10% of the sample particle sizes are smaller than this value, Dv50 means that 50% of the sample particle sizes are smaller than this value, and Dv90 means that 90% of the sample particle sizes are smaller than this value.
本发明测试方法通过峰面积或峰高的变化量/变化率等量化表征好氧颗粒污泥机械强度,在不同转速下对不同生物反应器生成的颗粒进行测试对比,具有普遍性和实用性。本发明可实现简便、精确的好氧颗粒污泥机械强度的量化表征及其标准化测试,形成标准化的数据体系,有利于不同反应器培养形成的好氧颗粒污泥机械强度的比较,为进一步提高反应器的稳定运行提供有益参考。The test method of the present invention quantitatively characterizes the mechanical strength of aerobic granular sludge by the change amount/change rate of peak area or peak height, and tests and compares the granules generated by different bioreactors at different rotation speeds, which is universal and practical. The present invention can realize simple and accurate quantitative characterization of the mechanical strength of aerobic granular sludge and its standardized test, forming a standardized data system, which is conducive to the comparison of the mechanical strength of aerobic granular sludge formed by different reactors, and provides a useful reference for further improving the stable operation of the reactor.
实施例2Example 2
以下结合具体实施例及附图,对本发明进一步作详细说明,但本发明的实施方式不限于此。除非特别说明,本发明采用的设备为本技术领域常规设备。The present invention is further described in detail below in conjunction with specific embodiments and drawings, but the embodiments of the present invention are not limited thereto. Unless otherwise specified, the equipment used in the present invention is conventional equipment in the art.
在2250r/min转速下,对反应器1中不同粒径(大、小)好氧颗粒污泥的机械强度测试。At a rotation speed of 2250 r/min, the mechanical strength of aerobic granular sludge with different particle sizes (large and small) in reactor 1 was tested.
一种测试好氧颗粒污泥机械强度的方法,包括以下步骤:A method for testing the mechanical strength of aerobic granular sludge comprises the following steps:
S1.采用激光粒度分析仪在不同转速下剪切好氧颗粒污泥样品,通过Dv10/50/90随作用时间变化图去除偏差较大的点;S1. Use laser particle size analyzer to shear aerobic granular sludge samples at different speeds, and remove points with large deviations through the Dv10/50/90 versus action time graph;
S2.绘制在等间隔作用时间t下的粒径分布变化图,横坐标为颗粒粒径(μm)、纵坐标为容量占比(%);S2. Draw a particle size distribution change diagram under equal interval action time t, with the abscissa being the particle size (μm) and the ordinate being the capacity percentage (%);
S3.从步骤S2中利用软件分析并提取峰面积变化率或变化量△S的信息,绘制出以作用时间为横坐标,峰面积变化率或变化量△S为纵坐标的散点图,拟合曲线,通过曲线量化表征好氧颗粒污泥的机械强度;峰面积变化率或变化量越小,表明颗粒在剪切过程中粒径变化较小,则好氧颗粒污泥的机械强度越好。S3. Analyze and extract the peak area change rate from step S2 using software Or the information of the change △S, plot the peak area change rate with the action time as the horizontal axis Or a scatter plot with the change △S as the ordinate, a fitting curve is formed, and the mechanical strength of the aerobic granular sludge is quantitatively characterized by the curve; the smaller the peak area change rate or change amount, the smaller the particle size change during the shear process, and the better the mechanical strength of the aerobic granular sludge.
其中,S为粒径分布与x轴围成的区域面积,即峰面积;t为粒径分布测试的作用时间。Wherein, S is the area enclosed by the particle size distribution and the x-axis, i.e., the peak area; t is the action time of the particle size distribution test.
本实施例中,步骤S1中,好氧颗粒污泥来自矩形膜生物反应器1(35×25×30cm),采用塑料网隔开形成体积比为2:1的好氧区和膜组件区;进水是由蔗糖(392.7mg/L)和其他营养物质组成的人工合成废水;所培养颗粒以丝状微生物为骨架,呈椭球状、表面光滑、棕褐色为主;样品分为两种不同颗粒粒径;转速设定为2250r/min,作用时间设置为50min,以2min进行等间隔时间测试;激光粒径分析仪遮光度设置为10-20,测试结果如图2,步骤S3分析得出的峰面积变化率随作用时间变化的拟合曲线图,见图3-a所示;In this embodiment, in step S1, aerobic granular sludge comes from a rectangular membrane bioreactor 1 (35×25×30cm), and is separated by a plastic mesh to form an aerobic zone and a membrane assembly zone with a volume ratio of 2:1; the influent is artificial synthetic wastewater composed of sucrose (392.7mg/L) and other nutrients; the cultured particles are based on filamentous microorganisms, ellipsoidal, smooth, and mainly brown; the samples are divided into two different particle sizes; the rotation speed is set to 2250r/min, the action time is set to 50min, and the test is performed at equal intervals of 2min; the shading degree of the laser particle size analyzer is set to 10-20, and the test results are shown in Figure 2, and the fitting curve of the peak area change rate obtained by analysis in step S3 versus the action time is shown in Figure 3-a;
将上述拟合出的曲线斜率进行比较,可看出相比大粒径,小粒径对应的曲线斜率较大,说明小粒径AGS的机械强度较弱。Comparing the slopes of the above fitted curves, it can be seen that the slope of the curve corresponding to the small particle size is larger than that of the large particle size, indicating that the mechanical strength of the small particle size AGS is weaker.
实施例3Example 3
在2250r/min转速下,对反应器2中好氧颗粒污泥的机械强度测试Mechanical strength test of aerobic granular sludge in
本实施例与实施例2相比,其区别在于:所用AGS不同,本实施例所用颗粒来自反应器2(4750×2500×3580mm),由曝气区和混合区组成,进水为生活污水,所培养颗粒主要是以钙离子为骨架,呈现内部颜色较浅、外部颜色较深;且不设置不同梯度粒径实验测试,作用时间设置为32min,测试结果见图2,步骤S3分析得出的峰面积变化率随作用时间变化的拟合曲线图,见图3-a;通过与实施例1的拟合曲线斜率比较,可以看出反应器2形成的AGS在较短作用时间内对应的曲线斜率最小,说明所形成AGS的机械强度最强。Compared with Example 2, the present embodiment is different in that the AGS used is different. The particles used in the present embodiment come from reactor 2 (4750×2500×3580 mm), which is composed of an aeration zone and a mixing zone. The influent is domestic sewage. The cultured particles are mainly based on calcium ions as the skeleton, showing a lighter internal color and a darker external color. No experimental test of different gradient particle sizes is set, and the action time is set to 32 min. The test results are shown in Figure 2. The fitting curve of the peak area change rate obtained by the analysis of step S3 versus the action time is shown in Figure 3-a. By comparing the slope of the fitting curve with that of Example 1, it can be seen that the AGS formed in
实施例4Example 4
在1500、2250、3000r/min转速下,对反应器1中好氧颗粒污泥的机械强度测试Mechanical strength test of aerobic granular sludge in reactor 1 at 1500, 2250 and 3000 r/min
本实施例与实施例2相比,其区别在于:设置不同梯度转速实验测试,但不设置不同梯度粒径实验测试,测试结果见图2,步骤S3分析得出的峰面积变化率随作用时间变化的拟合曲线图,见图3-b;通过对拟合曲线斜率的比较,可以看出反应器1所形成的AGS随转速逐渐增大拟合曲线斜率亦增大,说明AGS的机械强度在1500-3000r/min范围内随转速增大而下降。Compared with Example 2, the present embodiment is different in that: different gradient rotation speed experimental tests are set, but different gradient particle size experimental tests are not set. The test results are shown in Figure 2, and the fitting curve of the peak area change rate obtained by step S3 analysis versus action time is shown in Figure 3-b; by comparing the slopes of the fitting curves, it can be seen that the slope of the fitting curve of the AGS formed by the reactor 1 increases as the rotation speed gradually increases, indicating that the mechanical strength of the AGS decreases as the rotation speed increases within the range of 1500-3000r/min.
显然,本发明的上述实施例仅仅是为清楚地说明本发明所作的举例,而并非是对本发明的实施方式的限定。对于所属领域的普通技术人员来说,在上述说明的基础上还可以做出其它不同形式的变化或变动。这里无需也无法对所有的实施方式予以穷举。凡在本发明的精神和原则之内所作的任何修改、等同替换和改进等,均应包含在本发明权利要求的保护范围之内。Obviously, the above embodiments of the present invention are merely examples for clearly illustrating the present invention, and are not intended to limit the embodiments of the present invention. For those skilled in the art, other different forms of changes or modifications can be made based on the above description. It is not necessary and impossible to list all the embodiments here. Any modifications, equivalent substitutions and improvements made within the spirit and principles of the present invention should be included in the protection scope of the claims of the present invention.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211619970.0A CN116067846B (en) | 2022-12-15 | 2022-12-15 | A method for testing the mechanical strength of aerobic granular sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211619970.0A CN116067846B (en) | 2022-12-15 | 2022-12-15 | A method for testing the mechanical strength of aerobic granular sludge |
Publications (2)
Publication Number | Publication Date |
---|---|
CN116067846A true CN116067846A (en) | 2023-05-05 |
CN116067846B CN116067846B (en) | 2023-08-22 |
Family
ID=86169172
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211619970.0A Active CN116067846B (en) | 2022-12-15 | 2022-12-15 | A method for testing the mechanical strength of aerobic granular sludge |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN116067846B (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103196781A (en) * | 2013-04-15 | 2013-07-10 | 杭州师范大学 | Measuring method and device for mechanical strength of granular sludge |
CN103776780A (en) * | 2014-01-28 | 2014-05-07 | 杭州师范大学 | Method for detecting strength of granular sludge |
MY168903A (en) * | 2009-02-20 | 2018-12-04 | Univ Malaysia Teknologi | Procedure development for evaluation of aerobic granular sludge physical strength |
CN113479998A (en) * | 2021-04-27 | 2021-10-08 | 合肥工业大学 | Comprehensive evaluation method for aerobic sludge granulation degree |
-
2022
- 2022-12-15 CN CN202211619970.0A patent/CN116067846B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
MY168903A (en) * | 2009-02-20 | 2018-12-04 | Univ Malaysia Teknologi | Procedure development for evaluation of aerobic granular sludge physical strength |
CN103196781A (en) * | 2013-04-15 | 2013-07-10 | 杭州师范大学 | Measuring method and device for mechanical strength of granular sludge |
CN103776780A (en) * | 2014-01-28 | 2014-05-07 | 杭州师范大学 | Method for detecting strength of granular sludge |
CN113479998A (en) * | 2021-04-27 | 2021-10-08 | 合肥工业大学 | Comprehensive evaluation method for aerobic sludge granulation degree |
Non-Patent Citations (1)
Title |
---|
DANNY R. DE GRAAFF, ET AL: "Strength characterization of full-scale aerobic granular sludge", ENVIRONMENTAL TECHNOLOGY, vol. 41, no. 13, pages 1637 - 1647 * |
Also Published As
Publication number | Publication date |
---|---|
CN116067846B (en) | 2023-08-22 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN108640276A (en) | A kind of sewage treatment plant AAO process optimization operation methods based on WEST models | |
CN103471991B (en) | Activated sludge characteristic determination method based on zoogloea microscopical image analysis | |
CN113511723A (en) | Preparation method and application of a novel LDHs-based slow-release carbon source filler | |
CN103979824B (en) | Situ aggregation method preparation is for the microcapsule preparation method of cement-based material selfreparing | |
McCarthy et al. | Effect of Cell Morphology on Dead‐End Filtration of the Dimorphic Yeast Kluyveromycesmarxianus Var. marxianus NRRLy2415 | |
CN107686160A (en) | A kind of sewage water treatment method and system based on sbr reactor device | |
CN116067846A (en) | A method for testing the mechanical strength of aerobic granular sludge | |
US20200140301A1 (en) | Method for determining optimal preservation temperature of biofilm in wastewater treatment | |
Andras et al. | Test for characterizing settleability of anaerobic sludge | |
CN113109553B (en) | Asphalt binder fatigue resistance performance evaluation method and system | |
Bhattacharyya et al. | Understanding the mixing pattern in an anaerobic expanded granular sludge bed reactor: effect of liquid recirculation | |
CN119120635A (en) | A method for identifying granular sludge stability based on the characteristics of microbial activity changes | |
CN101419168A (en) | Activated sludge solubleness COD measuring method | |
Zhang et al. | Simple model of sludge thickening process in secondary settlers | |
CN117314270A (en) | Comprehensive evaluation method for marine environment monitoring information | |
CN115759795A (en) | Urban tourism ecological safety evaluation method based on fuzzy matter element model | |
CN110894101B (en) | A method for determining the optimum storage temperature of nitrification and denitrification biofilms for sewage treatment | |
CN109001435B (en) | Method for realizing accident early warning and management optimization of sewage treatment plant by adopting breathing pattern | |
CN113244893A (en) | Visible light response type solid waste adsorption-photocatalysis module for in-situ purification of endogenous organic pollution in lake and application | |
CN118304869B (en) | Preparation method and application of gel adsorption material of sodium alginate-embedded PNAGA-bamboo charcoal-green algae active cells | |
CN110835157A (en) | A method to determine the optimum storage temperature of aerobic granular sludge | |
CN115792194B (en) | Device and method for evaluating compatibility and air entraining quality of concrete air entraining agent | |
CN116626001B (en) | A method for determining the adsorption rate of sulfate-reducing bacteria on coal surface based on fluorescence spectrophotometry | |
CN115494011B (en) | Method for measuring adsorption performance of hard carbon material and application thereof | |
CN114460052B (en) | A method for direct detection of sodium pyruvate concentration based on fluorescent carbon quantum dots |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |