马尔文激光粒度仪简介

马尔文激光粒度仪简介
马尔文激光粒度仪简介

laParticle size analysis-Laser diffraction methods

(ISO-13320-1)

Introduction

Laser diffraction methods are nowadays widely used for particle sizing in many different applications. The success of the technique is based on the tact that it can be applied to various kinds of particulate systems, is fast and can be automated and that a variety of commercial instruments is available. Nevertheless, the proper use of the instrument and the interpretation of the results require the necessary caution.

Therefore, there is a need for establishing an international standard for particle size analysis by laser diffraction methods. Its purpose is to provide a methodology for adequate quality control in particle size analysis.

Historically, the laser diffraction technique started by taking only scattering at small angles into consideration and, thus, has been known by the following names:

-fraunhofer diffraction;

-(near-) forward light scattering;

-low-angle laser light scattering (LALLS).

However, the technique has been broadened to include light scattering in a wider angular range and application of the Mie theory in addition to approximating theories such as Fraunhofer and anomalous diffraction.

The laser diffraction technique is based on the phenomenon that particles scatter light in all directions with an intensity pattern that is dependent on particle size. All present instruments assume a spherical shape for the particle. Figure 1 illustrates the characteristics of single particle scattering patterns: alternation of high and low intensities, with patterns that extend for smaller particles to wider angles than for larger particles[2-7,10,15 in the bibliography].

Within certain limits the scattering pattern of an ensemble of particles is identical to the sum of the individual scattering patterns of all particles present. By using an optical model to compute scattering for unit volumes of particles in selected size classes and a mathematical deconvolution procedure, a volumetric particle size distribution is calculated, the scattering pattern of which fits best with the measured pattern (see also annex A).

A typical diffraction instrument consists of a light beam (usually a laser), a particulate dispersing device, a detector for measuring the scattering pattern and a computer for both control of the instrument and calculation of the particle size distribution. Note that the laser diffraction technique cannot distinguish between scattering by single particles and scattering by clusters of primary particles forming an agglomerate or an aggregate. Usually, the resulting particle size for agglomerates is related to the cluster size, but sometimes the size of the primary particles is reflected in the particle size distribution as well. As most particulate samples contain agglomerates or aggregates and one is generally interested in the size distribution of the primary particles, the clusters are usually dispersed into primary particles before measurement.

Historically, instruments only used scattering angles smaller than 14°,which limited the application to a lower size of about 1μm. The reason for this limitation is that smaller particles show most of their distinctive scattering at larger angles (see also annex Z).Many recent instruments allow measurement at larger scattering angles, some up to about 150°,for example through application of a converging beam, more or larger lenses, a second laser beam or more detectors. Thus smaller particles down to about 0.1μm can be sized. Some instruments incorporate additional information from scattering intensities and intensity differences at various wavelengths and polarization planes in order to improve the characterization of particle sizes in the submicrometre range.

Particle size analysis – Laser diffraction methods-

Part 1:

General principles

1 scope

This part of ISO 13320 provides guidance on the measurement of size distributions of particles in any two-phase system, for example powders, sprays, aerosols, suspensions, emulsions and gas bubbles in liquids, through analysis of their angular light scattering patterns. It does not address the specific requirements of particle size measurement of specific products. This

part of ISO13320 is applicable to particle sizes ranging from approximately 0.1

μm to 3μm.

For non-spherical particles, an equivalent-sphere size distribution is obtained because the technique uses the assumption of spherical particles in its optical model. The resulting particle size distribution may be different from those obtained by methods based on other physical principles (e.g. Sedimentation, sieving).

3,terms, definitions and symbols

For the purposes of this part of ISO 13320, the following terms, definitions and symbols apply.

3.1 terms, definitions

3.1.1 absorption

introduction of intensity of a light beam traversing a medium through energy conversion in the medium

3.1.2 coefficient of variation (变异系数)

Noative measure(%) for precision: standard deviation divided by mean value of population and multiplied by 100 or normal distributions of data the median is equal to the mean

3.1.3complex refractive index(Np)

Refractive index of a particle, consisting of a real and an imaginary (absorption) part.

Np=n p-ik p

3.1.4 relative refractive index (m)

complex refractive index of a particle, relative to that the medium。

3.1.5 deconvolution

Mathematical procedure whereby the size distribution of a particle ensemble is inferred from measurements of their scattering pattern.

3.1.6 diffraction

Spreading of light around the contour of a particle beyond the limits of its geometrical shadow with a small deviation from rectilinear propagation

3.1.7 extinction

Attenuation of a light beam traversing a medium through absorption and scattering .

3.1.8 model matrix

Matrix containing light scattering vectors for unit volumes of different size classes, scaled to the detector’s geometry, as derived from model computation.

3.1.9multiple scattering

Subsequent scattering of light at more than one particle, causing a scattering pattern that is no longer the sum of the patterns from all individual particles (in contrast to single scattering )

3.1.10 obscuration

Optical concentration

Percentage or fraction of incident light that is attenuated due to extinction (scattering and/or absorption) by the particles

3.1.11 optical model

Theoretical model used for computing the model matrix for optically homogeneous spheres with, if necessary, a specified complex refractive index, e.g. Frauhofer diffraction, anomalous diffraction, Mie scattering

3.1.12 reflection

Return of radiation by a surface, without change in wavelength

3.1.13 refraction

Change of the direction of propagation of light determined by change in the velocity of propagation in passing from one medium to another, in accordance with Snell’s law

N m sinθm=n p sinθp

3.1.14 scattering

General term describing the change in propagation of light at the interface of two media

3.1.15 scattering pattern

Angular or spatial pattern of light intensities[I(θ) and I(r) respectively] originating from scattering ,or the related energy values taking into account the sensitivity and the geometry of the detector elements

3.1.16 single scattering

Scattering whereby the contribution of a single member of variation (relative percentage) of the size distribution

NOTE for normal distributions about 95% of the population falls within ±2 standard deviations from the mean value and about 99.7% within ±3 standard deviations from the mean value.

3.2 symbols

4 principle

A representative sample, dispersed at an adequate concentration in a suitable liquid or gas, is passed through the beam of a monochromatic light source, usually a laser. The light scattered by the particles at various angles it measured by a multi-element detector and numerical values relating to the scattering pattern are then recorded for subsequent analysis. These numerical scattering values are then transformed, using an appropriate optical model and mathematical procedure, to yield the proportion of total volume to a discrete number of size classes forming volumetric particle size distribution.

5 Laser diffraction instrument

In the conventional set-up, a light source(typically a laser) is used to generate a monochromatic, coherent, parallel beam. This is followed by a beam processing unit, usually a beam expander with integrated filter, producing a extended and nearly ideal beam to illuminate the dispersed particles.

A representative sample, dispersed at an adequate concentration is passed through the light beam in a measuring zone by a transporting medium (gas or liquid); this measuring zone should be within the working distance of the lens used. Sometimes, the particle stream in a process is illuminated directly by the laser beam for measurement, as in the case of sprays, aerosols and air bubbles in liquids. In other cases (such as emulsions, pastes and powders), representative samples can be dispersed in suitable liquids (see annex C). Often dispersants (wetting agents: stabilizers) and /or mechanical forces (agitation; ultrasonication) are applied for deagglomeration of particles and stabilization of the dispersion. For these liquid dispersions a recirculating system is most commonly used, consisting

of an optical measuring cell, a dispersion bath usually equipped with stirrer and ultrasonic elements, a pump and tubing.

Dry powders can also be converted into aerosols through application of dry powder dispersers, which apply mechanical forces for deagglomeration. Here a dosing device feeds the disperser with a constant mass flow of sample. The disperser uses the energy of a compressed gas or the differential pressure to a vacuum to disperse the particles It outputs an aerosol that is blown through the measuring zone, usually into the inlet of a vacuum pipe that collects the particles.

There are two positions in which the particles can enter the laser beam. In the conventional case the particles enter the parallel beam before and within the working distance of the collecting lens [see Figure 3-a]. In the so-called reversed Fourier optics case the particles are entered behind the collecting lens and, thus, in a converging beam [see Figure 3-b].

The advantage of the conventional set-up is that a reasonable path length for the sample is allowed within the working distance of the lens. The second set-up allows only small path lengths but enables measurement of scattered light at larger angles, which is useful when submicrometre particles are present.

The interaction of the incident light beam and the ensemble of dispersed particles results in a scattering pattern with different light intensities at various angles (see annex a for theoretical background of laser diffraction), the total angular intensity distribution I(θ),consisting of both direct and scattered light, is then focused by a positive lens or an ensemble of lenses onto a multi-element detector. The lens(es) provide(s) for a scattering pattern which, within limits, is not dependent upon the location of the particles in the light beam. So, the continuous angular intensity distribution I(θ) is converted into a discrete spatial intensity distribution I(r) on a set of detector elements.

It is assumed that the recorded scattering pattern of the particle ensemble is identical to the sum of the patterns from all individual single scattering particles presented in random relative positions. Note that only a limited angular range of scattered light is collected by the lens(es) and, thus, by the detector.

The detector generally consists of a number of photodiodes; some instruments apple one photodiode in combination with moving slits. The photodiodes convert the spatial intensity distribution I(r) into a set of photocurrents I n, subsequent electronics then convert and digitize the photocurrents into a set of intensity or energy vectors L n. Representing the scattering pattern. A central element measures the intensity of the non-scattered light and, thus, with a calculation, provides a measure of optical concentration or obscuration. Some instruments provide special geometries of the central element in order to automatically re-centre or re-focus the detector by moving the detector or the lens. It is desirable that the detector elements are positioned so as to prevent the light reflected from the surface from re-traversing the optical system.

A computer controls the measurement and is used for storage and manipulation of the detected signals, for storage and/or calculation of a proper form of the optical model (usually as a model matrix containing light scattering vectors per unit of volume per size class, scaled to the detector’s geometry and sensitivity) and calculation of the particle size distribution (see annex a for theoretical background of laser diffraction). Also it may provide automated instrument operation.

Several significant differences exist, both in hardware and software, not only between instruments from different manufacturers but also between different types from one company. The instrument specifications should give adequate information for proper judgement of these differences. In annex B recommendations are presented for the specifications of laser diffraction instruments.

6 operational procedures

6.1 requirements

6.1.1 instrument location

The instrument should be located in a clean environment that is free from excessive electrical noise, mechanical vibration, and temperature fluctuations and is out of direct sunlight. The operating area should be well ventilated. The instrument should either contain a rigid internal optical

bench or be installed on a rigid table or bench to avoid realignment of the optical system at frequent intervals.

Warning:the radiation of instruments equipped with a low power laser can cause permanent eye damage. Never look into the direct path of the laser beam or its reflections. Avid cutting the laser beam with reflecting surfaces. Observe the local laser radiation safety regulations.

6.1.2 dispersion liquids

Any optically transparent liquid of known refractive index may be used. Thus, a variety of liquids is available for preparation of liquid dispersions of powders. Annex c provides requirements for the dispersion liquids.

If an organic liquid is used for dispersion, observe the local health and safety regulations. Use a cover for the ultrasonic bath when using liquids with a high vapour pressure in order to prevent the formation of hazardous vapour concentrations above the bath and/or the generation of low-temperature zones with fluctuating refractive indices in the fluid by evaporation.

6.1.3 dispersion gases

For dry dispersion and spray applications a compressed gas is sometimes used. If used, it is essential that it is free from oil, water and particles. To achieve this, a dryer with a filter is required. Any vacuum unit should be located apart from the measurement zone, so that the output of the hot air does not reach the measuring zone, draught should be avoided in order to avoid unstable particulate streams.

6.2 Sample inspection, preparation, dispersion and concentration

6.2.1 sample inspection

Inspect the material to be analysed, visually or with the aid of a microscope, firstly to estimate its size range and particle shape and later to check whether the particles have been dispersed adequately.

The size distribution measured in a sample is only valid for a batch of material if the sample is representative for that batch and dispersed adequately.

6.2.2 preparation

For dry powders, prepare a representative sample of suitable volume for the measurement by an adequate sample splitting technique, for instance a rotating riffler. If very small samples are required, or in the case of wet powders, it is also possible to take fractional samples out of a well-mixed

sample paste. The consistency of the paste then avoids segregation errors. The pastes are formed by adding dispersant to the sample drop by drop while mixing it with a spatula. As long as the mixture forms lumps, single drops should be added while continuing the mixing after each drop.

A good consistency for the paste is one like honey or toothpaste. If the paste becomes too fluid by mistake, it shall not be used, and a new preparation should be initiated.

If the maximum size exceeds the measuring range, remove the material that is too coarse, e.g. by presieving. In this case determine and report the amount/percentage removed.

Sprays, aerosols and gas bubbles in liquid should be measured directly, provided that their concentration is at an adequate level (see 6.2.3 and

6.2.4) ,since sampling or dilution is generally impossible without altering the particle size distribution.

6.2.3 Dispersion

6.2.3.1 Dry powders can be dispersed either in air or in liquid. The dispersion procedure shall be adjusted to the purpose of the measurement, e.g. It has to be decided whether agglomerates should be detected or broken down to the primary particles

6.2.3.2 An adequate dry disperser should be applied; here, generally compressed air or vacuum is applied for dispersion by shear stress with the assistance of mechanical de-agglomeration by particle-particle or particle-wall collisions(see figure 4). For dry dispersion, the complete fractional sample shall be used for the measurement. Note that the use of large sample quantities can overcome the poor statistical representation of coarse particles in a wide size distribution. It is necessary to check that comminution of the particles does not occur and conversely that a good dispersion has been achieved. This is usually done by direct comparison of dry dispersion with a liquid one: ideally, the results should be the same. Another possibility for checking the degree of dispersion or comminution is by changing the dispersing energy (e.g. The primary air pressure) and monitoring the change of the size distribution. Usually upon increasing the dispersing energy the amount of fines is increased at first, due to improved dispersion, until a plateau is reached, where the size distribution is nearly constant with increasing energy. At still higher energies the amount of fines may rise again as a result of comminution. On some occasions, agglomeration has been found at high flow rates through a cascade. The

centre of the plateau define the optimum dispersing energy. Note, however, that a plateau is not always found (for instance for highly aggregated or fragile particles).

6.2.3.3 For the preparation of liquid dispersions a variety of liquids is available. Annex C presents requirements and some advice. Generally, pasting, stirring and ultrasonication can be used to facilitate proper dispersion of particles in the liquid. A preliminary check on the dispersion quality can be made by visual/microscopic inspection of the suspension. Also, it is possible to perform some measurements of the suspension in the laser diffraction instrument, with intermediate ultrasonication: the measured size distribution should not change significantly if the sample is well dispersed and the particles are neither fragile nor soluble.

The minimum volume of sample , required for repeatable measurement, increases as the width of the size distribution becomes greater in order to allow a sufficient number of large particles to be present. Accordingly, the volume of the dispersion fluid required to suspend these samples also increases if the limits of optical concentration are to be observed.

For example, for a sample with particles in the approximate size range of 2μm to 200μm, a sample volume of at least 0.3 ml is needed. This will require at least 500ml of suspension fluid for its dispersion. Also, the measurement time or the number of detector readings within one measurement should be sufficient to reach a reasonable precision. Appropriate measurement conditions should be established experimentally, in relation to the desired precision.

6.2.4 Concentration

The particle concentration in the dispersion should be above a minimum level, which for many instruments will correspond to about 5% obscuration, in order to produce an acceptable signal-to-noise ratio in the detector. Likewise, it should be below a maximum level, which for many instruments will correspond to about 35% obscuration for particles larger than about 20

μm, in order to avoid multiple scattering (where light is scattered subsequently at more than one particle).

For particles smaller than about 20μm, the obscuration value should be kept below about 15% for the same reason. In general, multiple scattering appears at larger scattering angles. Without multiple scattering correction, the amount of fines calculated will exceed the true value. If work at higher concentrations is required, it should be possible to correct for multiple scattering or systematic errors will arise. A first estimate for the concentration can be reserved from figure 5.

Figure 5, though only an example, shows that the optimum particulate concentration is nearly proportional to the circle size: smaller particles require lower concentrations. For instance, particles with a diameter of about 1μm fire volumetric concentrations during measurement of about 0.002%, whereas the concentration for 100μm circles should be about 0.2%, in a cell with a 2mm path length. As a consequence, the width of the particle size distribution influences the optimum sample concentration for measurement. Moreover, the range of concentrations, shown in figure 5, is influenced by the laser beam width, the path length of the measurement zone, the optical perties of the particles and the sensitivity of the detector elements.

New of the above, measurements should be performed at different particulate concentrations in order to decide be optimum concentration range for any typical sample of material.

6.3 measurement

6.3.1 procedure

Optical measurement of a particle size distribution by laser diffraction comprises the following steps:

a ) setting up instrument and blank measurement

After selection of the appropriate particle size range and proper alignment of the optical part of the instrument. The blank measurement is performed in which a particle-free dispersion medium is used. Detector data are saved in order to subtract them later from the data obtained with that sample in order to obtain net sample signals.

b ) measurement the scattering pattern of dispersed sample(s)

Generally, a measuring time allowing for a large number of detector scans or sweeps at short time intervals is used: typically some 2 seconds or 1000 sweeps. For each detector element an average signal is calculated, sometimes together with its standard deviation. Data are store in the computer memory. The magnitude of the signal from each detector element depends upon the detection area, the light intensity and the quantum efficiency. The coordinates (size and position) of the detector elements together with the focal distance of the lens determine the region of scattering angles for each element. Generally all these factors are factory determined and stored in the computer.

Most instruments also measure the intensity of the central laser beam. The fractional difference between a dispersed sample and a blank experiment is given as an obscuration value, which is indicative of the total amount of scattered light and the particle concentration.

c ) selection of an appropriate optical model

Most often either the fraunhofer or the Mie theory is used.

Sometimes other approximating theories are applied for calculation of the scattering matrix. When using the Mie theory, the refractive indices of particulate and medium, or their ratio, should be brought into the instrument in order to allow calculation of the model matrix (see annex D for the refractive indexes of liquids and solids). Often , small values of the imaginary part of the refractive index (about 0.01-0.1) are applied to cope with the surface roughness of the particles.

NOTE: small differences in the assumed complex refractive index may cause significant differences in resulting particle size distributions..

In order to obtain traceable results it is essential that the refractive index values used are reported

d ) conversion of scattering pattern into particl

e size distribution

This deconvolution step is the inverse of the calculation of a scattering pattern for a given particle size distribution. The fact that short measured data always contain some random and systematic errors, may cause erroneous size distribution results. Several mathematical procedures have

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2.5 相关名词解释 2.5.1 粒径:又称颗粒尺寸,用以表征颗粒的大小。除了球形颗粒这一特例外,粒径并不是真实的物理尺寸,而是会随测量原理变化的等效尺寸。在激光散射法技术中,粒径是指与待测颗粒有相同的化学性质并有最相近的光散射特性的球形颗粒(组合)的直径(分布)。 2.5.2 粒度分布:是指一个粉体样品中各种粒径的颗粒所占的比例。因为任何一个粉体样品都是由大小不同的颗粒组成的,所以用粒度分布才能确切地描述其粗细情况。 2.5.3 悬浮介质:测量粒度时需要把样品分散在液体或气体中。这里的液体或气体就称为悬浮介质。合适的悬浮介质应该是既能让样品在其中分散,又不让样品在其中分解或发生化学反应的。 2.5.4 光能分布:即散射光的能量分布,就是照射到粒度仪各光电探测器上的散射光的能量。背景光能代表被光路上的尘埃粒子或各光学镜面的疵点散射的光能分布;而样品颗粒的散射光能是被待测样品的颗粒散射的光能,其分布与样品颗粒的粒度相对应,但不等于粒度分布。 2.5.5 遮光比:指测量用的照明光束被测量的样品颗粒阻挡的部分与照明光的比值。颗粒在测量介质中的浓度越高,则遮光比越大。 2.5.6 平均粒径:是指样品中所有颗粒的粒径的平均值,可以根据粒度分布计算而得。 2.5.7粒度分布宽度:用以表征样品粒径的均匀程度。粒度分布宽,表示样品颗粒的粗细不均匀;反之,则表示均匀。 2.6 准备阶段 2.6.1系统开机 打开电源开关 测量单元(预热半小时后进行下面步骤) 循环进样器 打印机 显示器 计算机主机 2.6.2 测量单元预热 2.6.2.1如关机超过半小时再重新开机,必须预热半小时。 2.6.2.2打开测量单元电源,半小时后,激光率才能稳定。如果环境温度较低,等待时间还要延长。 2.6.2.3判断激光功率是否达到稳定的依据是,背景光能分布的零环高度是否稳定。正常

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1、目的:建立BT-2003激光粒度分布仪的操作规程,使检验人员正确BT-2003激光粒度分布仪。 2、适用范围:适用于粒径的测定。 3、责任人:化验员。 4、正文: 4.1基本操作: 4.1.1开机顺序:激光粒度分布仪→自动循环分散系统→启动粒度分析软件。4.1.2关机顺序:关闭粒度分析软件→自动循环分散系统→激光粒度分布仪。4.1.3常规操作时的操作步骤。 4.1.3.1测试准备:(1)填写“文件-数据库处置”信息。(2)点击“下一步”进入“测试参数”:选择合适的物质(如碳酸钙)、介质(水)等。在选择合适的分析模式。(3)下一步进入点“常规测试”进入测试窗口。(4)单击“进水”图标把循环池加满水,然后交替的循环泵和超声波消除气泡(至少3次),再开启超声、循环。 4.1.3.2开始测试:(1)背景:启动“测量-常规测试”测量系统背景。背景高度应在0.5-5之间(1-4最佳),横坐标长度小于20格,20格以后没有信号。点击“确认”后背景将被保存下来。(2)浓度:观察遮光率,这个值一般应在10%-15%之间。(3)分散:超声分散3分钟左右。(4)测试:点击“连续”按钮开始测试并显示结果。(5)保存和打印:点击保存或打印按钮,将结果保存到数据库里,测试结束。 4.1.3.3清洗:点击“自动清洗”图标清洗循环分散系统,然后准备进行下次测试。 4.1.4自动测试时的操作步骤: 4.1.4.1SOP设置:打开“文件-数据库处置”填好内容后点击下一 步进入测试参数后点击“自动流程”设置里面的各项参数后点“确认”保存下来,点击“自动测试”进入自动测试窗口后即可以进行自动测试。 4.1.4.2自动测试:点击“自动测试”按钮,待提示请加入样品时加入适量的样品(遮光率为10%-15%),就等待结果即可。 4.2准确性标定方法: 4.2.1标定周期:通常半年标定一次,仪器经过维修后要标定

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!!! 注意:进行测量之前必须塞住塞子 4、持样品池顶部,远离下部测量区,将样品池推入样品槽至其停止。 5、关闭样品池区盖子。 !!! 注意:虚线方向为正面 四、 测试 1、粒度测试 1)双击桌面上的DTS(nano)打开软件 2)选择File>New>Measurement File创建新的测量记录文件,保存在D盘 ‐data of DLS‐组内/组外。

对于已经存在测试文件,请选择Open打开文件 3)打开测试文件后,选择File>New>SOP或者File>Open>SOP来新建或者调出 标准测量程序。对于不常测试的样品,可以选择Measure>Manual来进行手动测 量设置。 3)新建SOP,选择File>New>SOP或者手动创建测量程序是会跳出如下对话框

4)左键点击? Measurement type,然后从下拉菜单中选择测量类型,粒径测量 我们选择Size。 4)按右向箭头,依次输入样品的概述 (编号和样品名称,样品的折光指数和吸收率)

马尔文MS3000粒度仪

超高速智能粒度分析仪 粒度引领粒度分析技术新时代 Mastersizer 3000 马尔文仪器(中国)

Mastersizer 3000不仅仅是一台新仪器—它是全新的粒度测量大师 马尔文仪器公司于1970年推出世界第一台商用激光粒度仪。随后第一套Mastersizer 系统在1988年诞生,自此,马尔文仪器一直引领着激光衍射粒度分析领域的发展。我们投身于这一技术,并为世界各地超过10,000家的Mastersizer 用户带来最新的技术、应用和各种粒度分析解决方案。 The Mastersizer 3000 最高性能、最小体积 Mastersizer 3000—最先进的系统 快速、可靠且高度自动化的激光衍射技术已经成为了世界上使用最广泛的粒度分析技术。现在,Mastersizer 3000将引领激光衍射技术步入全新的高速智能时代。 2

3 Mastersizer 3000的优势 Mastersizer 3000仪器及其分散系统的创新设计和革新工艺体现了马尔文公司的热诚和专业。我们根据市场需求开发了在最小的空间中包含最全面性能的仪器。快速而准确,Mastersizer 3000让所有人都能得心应手,无论是新用户还是粒度分析专家。 The Mastersizer 3000

革新的光学核心 Mastersizer 3000利用经过验证的激光衍射技术测定颗粒粒径。根据测定样品产生的在不同角度上的衍射光强度分布来计算粒度分布。采集这些数据所需的光学系统是本仪器的核心。 在新型的折叠光路设计中,Mastersizer 3000中的蓝光固态光源保证了亚微米级的分辨率,使粒径分析下限达到10nm。高速的数据采集速率大大增加了测试中的信号采集次数,提高了分析的重现性,即使是分布最宽的样品也能精确测定。同时也显著提高了测试速度。总之,依靠该独特的光学系统,仅一台仪器即可在整个极宽的动态范围内获得值得信赖的粒径数据。 The Mastersizer 3000 2 46 6 7 3 4

12-激光粒度仪标准操作规程

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图2、“文档”窗口 图3、测试参数 光学参数:使用Mie散射理论进行数据处理。 折射率:激光粒度分析中的基本理论——米氏散射理论需要折射率参数。

操作 图4、常规测试窗口 状态(背景状态良好)。如果背景数值和状态正常,在“背景操作区”中单击“确认”就完成背景测试;如果背景值和状态不正常,单击“背景校准”系统将进入背景校准窗口,进行调整背景;“默认”是用上一次的背景值,此功能常用于测试过程中关闭测试窗口又重新进入不能重新测试背景时;“启动”是在按确认后需要重新测试背景时使用。图5是背景数据不正常时的几种情形及原因: 将样品混合均匀,用小勺在样品袋中的不同部位不同深度各取少量多次加

遮光率调整:①遮光率太高时:应在充分循环均匀的条件下排放掉一部分悬浮液,然后加水稀释,直到遮光率合适为止。克服遮光率过高的有效方法就是“少量多次”加样。②遮光率太低时:再向循环池中加适量的样品,直到遮光率合适并从最后一次加样算起图5、几种不正常的背景状况及原因 光路偏移-需要校准 样品池或透镜脏 介质不纯净或透镜脏 图6、常规测试界面说明 遮光率指示 散射光强坐标 探测器坐标

图7、测试窗口图8、“实时”窗口单次:在图7中单击“单次”按钮,将得到一次的测试结果。 就按它! 图9、单次测试 ?连续:在图7中单击“连续”按钮,将得到多次测试结果。 就按它! 图10、连续测试 ?图形设置:在图7中单击“图形设置”按钮,将可以设置测试区中光能信号图形显 示方式:柱型图、曲线、对比信号的比例和颜色,如图11。“对比信号”是指当前信号对比上一次测试的测量信号,启用后测试区同时显示两组信号。

马尔文MS2000SM 激光粒度仪 操作程序-标准版

马尔文MS2000操作程序 一.开机顺序:先开仪器主机和湿法进样器,再开电脑软件。 关机顺序:先关电脑软件,再关湿法进样器和主机。二.湿法测量程序: a)往进样器加水,调节控制盒,让水循环起来,搅拌速度调到2500。 b)在桌面上双击Mastersizer2000操作软件,进入操作软件,输入操作者姓名,然后鼠标左键点击确定,开机预热30分钟以后才能进行测量样品。 c)在“文件File”那里点击打开,打开已有的文件或新建一个文件,确保测量记录存放在你所需要的文件名下。 d)单击“测量Measure”菜单中的“手动Manual”按钮,进入测量窗口。 e)然后点击“对光Align”,对光好后,如果背景Background状态正常,(如果Detector Number那边的信号基本成左边高右边低的态势就是比较正常的背景)就不需要换水了,如果换了几次水以后,背景还是不正常,就需要打开样品池窗口进行清洁样品窗口。(如果是第一次打开软件的话,“对光Align”按键是隐藏在“测量背景Measure Background”下面的,只要点击“开始Start”键盘,仪器就会对光接着测量背景的)。 f)然后进入“选项Options”菜单,选择合适的光学参数,在“物质Material”那的“物质名称Sample material name”那里选择好

样品的物质名称,如果测量的是仪器配的标准样品,要求选择“Glass Beads”,在“分散介质Dispersant name”选择Water,“模型Models”选择“通用模式General purpose”,如果是测量标准样品要求选择“single mode”,“颗粒形貌Particle shape”选择“不规则Irregular”,标准样品要求选择“spherical”,“测量选项Measurement”那里选择“样品测量时间Sample measurement”8秒,“背景测量时间Background measurement”10秒,在“测量循环Measurement Cycles”选择“测量次数Number of measurement cycles”3次,“延时时间Delay between measurement”选择0秒,下面的“创建平均结果Average Result”选择创建。再进入“文档Documentation”菜单,输入样品名称,然后确定退出。 g)然后单击“开始Start”按钮,系统开始测量背景,当背景测量完成以后并提示“加入样品Add Sample”后,开始加入样品到“遮光度Laser Obscuration”到10%左右,等待样品分散10秒,然后单击“开始Start”或按“测量样品Measure Sample”进行测量样品。每测量一次,结果会按照记录编号顺序自动存在文件里。 h)测量结束后,调节控制盒速度到0,打开排水手柄,让水排完以后,然后换新鲜的水循环清洗两到三次(以对光后背景正常为准)。

激光粒度仪操作步骤

一:设置测试条件,点击测量,弹出“测量设置”,输入参数。 1)标识(zhì):输入样品名称 2)颗粒类型:用于创建散射模型 3)物质:根据样品材料,设置颗粒折射率,吸收率。用于创建散射模型 4)分散剂:根据分散介质,设置其折射率。用于创建散射模型 5)说明:输入备注文档,例如测试注意事项,分散条件等 6)测量时间:输入背景测量时间和样品测量时间。时间长短取决于散射光信号强 度和稳定性(信噪比) 7)顺序:设置重现性测试次数 8)遮光度:通过设置遮光度范围,控制加样浓度,以避免因浓度过低导致信噪比 差和浓度过高引起的多重光散射。 9)样品分散附件:根据样品不同,设置不同的进样器分散条件 10)清洗样品池:设置样品池清洗方式 11)数据处理与分析:根据分散介质,设置其折射率,根据样品特征,选择合适的 分析模型。用于创建散射模型。 12)结果:选择粒径结果显示范围和分布类型 13)用户粒度分级:数据输出 14)平均:由若干次重现性测试记录,创建平均结果 15)打印 二:测试设置后,点击“确定”键,开始测试 左上角处图谱显示各检测器即时信号,横坐标为检测器编号,编号越大,散射角越大,代表小颗粒的散射光。 三:测试步骤: 1)启动进样器,是分散介质正常流动。 2)以自动或手动方式对光,保证各个检测器位置(散射角)准确。 3)测量无激光时的背景,即电子背景,扣除检测器暗电流。 4)测量光学背景:监测并扣除非样品导致的散射光信号。好的背景呈现递减趋势, 说明分散介质中杂质、气泡含量较少,未引起过多的散射光。背景信号属于测量的噪音信号,所以应稳定并尽量低。 5)准备加样,此事显示信号为扣除背景信号后的随机信号,需检查各个检测器信 号随机变化,相互无关联。 6)加样,同时注意左侧遮光度变化,在达到设定后停止加样,并点击开始测试。 7)测试时,会显示测试结果和结果趋势图。 8)完成测试后,检测器检测到散射光数据,在扣除背景后,显示在“数据”报告 中 9)散射光数据代入散射模型中,进行反演运算,运算过程显示在拟合报告中。 10)在分析报告中,可以看到测量得到的粒径分布结果,包括图谱,分级列表和特 征值。

应用马尔文激光粒度仪分析泥沙数据处理模板

Journal of Water Resources Research 水资源研究, 2015, 4(6), 513-521 Published Online December 2015 in Hans. https://www.360docs.net/doc/263429950.html,/journal/jwrr https://www.360docs.net/doc/263429950.html,/10.12677/jwrr.2015.46064 文章引用: 田岳明, 沙剑. 应用马尔文激光粒度仪分析泥沙数据处理模板[J]. 水资源研究, 2015, 4(6): 513-521. A Sediment Data Processing Template for Malvern Laser Particle Size Analyzer Yueming Tian 1, Jian Sha 2 1Hydrological Bureau of the Yangtze River Water Resources Commission, Wuhan Hubei 2 Hydrology and Water Resources Survey Bureau of the Yangtze River Estuary in Shanghai, Shanghai Received: Nov. 8th , 2015; accepted: Nov. 27th , 2015; published: Dec. 10th , 2015 Copyright ? 2015 by authors and Hans Publishers Inc. This work is licensed under the Creative Commons Attribution International License (CC BY). https://www.360docs.net/doc/263429950.html,/licenses/by/4.0/ Abstract Malvern laser particle size analyzer has been applied in the particle analysis of river sediments since the beginning of this century, and has been highly praised by users for simple operation, stable data from analysis, high automation of processing and quick achievements, etc. regardless of its significant devia-tion from the principles of traditional sedimentation analysis approach [1]. Now, it has been applied and popularized in the particle analysis of river sediments. Nevertheless, users may run into some problems in the use of this equipment, such as, inconvenient setting and check of fundamental parameters, lack of automatic detection and warning about quality of test data, troublesome selection of characteristic and extreme values in the data of tested particle grading, inconsistent form of analysis report, and cumber-some reading and output of data, etc. To solve these problems and unify the principles and requirements for operation of laser analyzer at the sediment monitoring stations, a “sediment data processing tem-plate for Malvern laser particle size analyzer” is developed while making full use of the existing functions of laser analyzer. This template is able to configure the fundamental parameters automatically, check the quality of analytic data and give warnings, print the reports in standard form according to the code of each monitoring station, and generate the textual output of analytic data in batches, etc., which can be directly sorted out and edited in the Southern Hydrological Data Processing (SHDP) software. The opera-tion for several years has achieved favorable effects, improved working efficiency, reduced error rate and ensured the quality of achievements. Keywords Laser Particle Size Analyzer, Sediment Analysis, Data Processing, Research Template 作者简介:田岳明(1959-),男,长江水利委员会水文局,高级工程师,主要从事河流泥沙粒度分析技术管理与研究。

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