[go: up one dir, main page]

CN107870136A - A kind of assay method of amphion sulfonated phenol formaldehyde resin cationic degree - Google Patents

A kind of assay method of amphion sulfonated phenol formaldehyde resin cationic degree Download PDF

Info

Publication number
CN107870136A
CN107870136A CN201610858002.3A CN201610858002A CN107870136A CN 107870136 A CN107870136 A CN 107870136A CN 201610858002 A CN201610858002 A CN 201610858002A CN 107870136 A CN107870136 A CN 107870136A
Authority
CN
China
Prior art keywords
amphion
formaldehyde resin
phenol formaldehyde
solid
sulfonated phenol
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
Application number
CN201610858002.3A
Other languages
Chinese (zh)
Other versions
CN107870136B (en
Inventor
黄宁
孟丽艳
张希红
史康玲
常建芳
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sinopec Oilfield Service Corp
Sinopec Zhongyuan Petroleum Engineering Co Ltd
Drilling Engineering Technology Research Institute of Sinopec Zhongyuan Petroleum Engineering Co Ltd
Original Assignee
Sinopec Oilfield Service Corp
Drilling Engineering Technology Research Institute of Sinopec Zhongyuan Petroleum Engineering Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sinopec Oilfield Service Corp, Drilling Engineering Technology Research Institute of Sinopec Zhongyuan Petroleum Engineering Co Ltd filed Critical Sinopec Oilfield Service Corp
Priority to CN201610858002.3A priority Critical patent/CN107870136B/en
Publication of CN107870136A publication Critical patent/CN107870136A/en
Application granted granted Critical
Publication of CN107870136B publication Critical patent/CN107870136B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N5/00Analysing materials by weighing, e.g. weighing small particles separated from a gas or liquid
    • G01N5/02Analysing materials by weighing, e.g. weighing small particles separated from a gas or liquid by absorbing or adsorbing components of a material and determining change of weight of the adsorbent, e.g. determining moisture content

Landscapes

  • Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Pathology (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)

Abstract

本发明涉及化学分析技术领域,具体涉及一种两性离子磺化酚醛树脂阳离子度的测定方法,包括首先测定每0.5g纯净的两性离子磺化酚醛树脂在硅藻土中的吸附量m,然后带入公式A=863.87m‑24.54,计算得出两性离子磺化酚醛树脂的阳离子度A。本发明根据两性离子磺化酚醛树脂分子链上的阳离子季铵盐基团具有良好的吸附性能,利用硅藻土作为标准吸附介质对待测样品吸附前后质量的变化计算吸附质量,这种基于吸附称重法的阳离子度测定方法,避免了现有技术中阴离子对测定过程和测定结果的影响,提高检测结果的准确性,并且具有广泛的适用性和较强的可操作性,而且仪器设备条件要求低,能在常规检测实验室推广应用。

The invention relates to the technical field of chemical analysis, in particular to a method for determining the cationicity of zwitterionic sulfonated phenolic resins, comprising first measuring the adsorption capacity m of every 0.5 g of pure zwitterionic sulfonated phenolic resins in diatomite, and then Bring in the formula A=863.87m-24.54 to calculate the cationic degree A of the zwitterionic sulfonated phenolic resin. According to the cationic quaternary ammonium salt group on the molecular chain of the zwitterionic sulfonated phenolic resin, which has good adsorption properties, the present invention uses diatomite as a standard adsorption medium to calculate the adsorption mass according to the change in the mass of the sample to be tested before and after adsorption. The cationic degree determination method of the gravity method avoids the influence of anions on the determination process and measurement results in the prior art, improves the accuracy of the detection results, and has wide applicability and strong operability, and the equipment conditions require Low, can be popularized and applied in routine testing laboratories.

Description

一种两性离子磺化酚醛树脂阳离子度的测定方法A kind of determination method of cationic degree of zwitterionic sulfonated phenolic resin

技术领域technical field

本发明涉及化学分析技术领域,具体涉及一种两性离子磺化酚醛树脂阳离子度的测定方法。The invention relates to the technical field of chemical analysis, in particular to a method for measuring the cationic degree of zwitterionic sulfonated phenolic resin.

背景技术Background technique

近年来,随着钻井液处理剂的发展,阳离子聚合物处理剂以其优良的抑制防塌性能在解决井壁失稳、粘土矿物对钻井液污染等问题上表现出良好的应用效果,减少了井下复杂和降低钻井综合成本,是油田化学工作者关注的研究热点之一。两性离子磺化酚醛树脂是在磺化酚醛树脂基础上,引入阳离子基团的合成树脂,由于分子链中引入了阳离子基团,增加了产品的抑制、防塌性能,被作为一种常用钻井液处理剂广泛使用。In recent years, with the development of drilling fluid treatment agents, cationic polymer treatment agents have shown good application effects in solving problems such as wellbore instability and clay mineral pollution to drilling fluids due to their excellent inhibition and anti-slump properties, reducing the Downhole complexity and reduction of comprehensive drilling costs are one of the research hotspots of oilfield chemists. Zwitterionic sulfonated phenolic resin is a synthetic resin based on sulfonated phenolic resin and introduced cationic groups. Due to the introduction of cationic groups in the molecular chain, the inhibition and anti-slump performance of the product are increased, and it is used as a common drilling fluid. Treatment agents are widely used.

两性离子磺化酚醛树脂中引入的阳离子基团含量的多少,在很大程度上决定了其抑制防塌性能,通常也会以其阳离子度为标准来选择适用的两性离子磺化酚醛树脂。然而,两性离子磺化酚醛树脂分子链上含有大量的强阴离子水化- SO3 2-基团,常规聚合物阳离子度测定方法为化学分析法,包含:四苯硼钠滴定法、胶体滴定法、磷钨酸容量法都因其强阴离子水化-SO3 2-基团的排斥作用,无法与沉淀剂或阴离子聚电解质形成沉淀或电中和反应。文献《钻井液用两性离子磺甲基酚醛树脂阳离子度的测定方法初探》指出四苯硼钠滴定法对于有色的两性离子磺甲基酚醛树脂不适用,原因在于滤液颜色对指示剂终点判断的干扰。而实际上,内在原因是两性离子磺甲基酚醛树脂分子结构中大量的磺酸基团对四苯硼酸根的排斥作用,导致不能充分产生季铵盐沉淀,而不能准确测定阳离子度。即使采用四苯硼钠重量法也同样存在上述现象,引起较大的测定偏差。企标Q/SH1025 0779-2011《钻井液用两性离子磺甲基酚醛树脂通用技术条件》中虽然先通过阳离子交换树脂欲将阴离子磺酸基团洗脱掉,但试验操作过程中不仅阴离子基团存在较低的洗脱率而且阳离子基团会有损失,导致磷钨酸容量法产生较大的测定偏差。The amount of cationic groups introduced into the zwitterionic sulfonated phenolic resin largely determines its anti-slump performance, and the suitable zwitterionic sulfonated phenolic resin is usually selected based on its cationic degree. However, the molecular chain of the zwitterionic sulfonated phenolic resin contains a large number of strong anionic hydration - SO 3 2- groups. The conventional method for determining the cationicity of polymers is chemical analysis, including: tetraphenylborate sodium titration, colloid titration and phosphotungstic acid volumetric method are unable to form precipitation or neutralization reaction with precipitant or anionic polyelectrolyte because of the repulsion effect of strong anionic hydration -SO 3 2- group. The literature "Preliminary Study on the Determination of Cationic Degree of Zwitterionic Sulfomethylphenol Formaldehyde Resin for Drilling Fluid" points out that the sodium tetraphenylborate titration method is not suitable for colored zwitterionic sulfomethylphenol formaldehyde resin, because the color of the filtrate interferes with the judgment of the end point of the indicator . In fact, the internal reason is that a large number of sulfonic acid groups in the molecular structure of the zwitterionic sulfomethylphenol-formaldehyde resin repel the tetraphenylborate, resulting in the inability to fully produce quaternary ammonium salt precipitation, and the degree of cation cannot be accurately measured. Even if the sodium tetraphenylborate weight method is used, the above phenomenon also exists, causing a large measurement deviation. Enterprise Standard Q/SH1025 0779-2011 "General Technical Specifications for Zwitterionic Sulfomethylphenolic Resins for Drilling Fluids" Although the anionic sulfonic acid groups are first eluted through the cation exchange resin, but not only the anionic groups There is a low elution rate and the loss of cationic groups, resulting in a large measurement deviation of the phosphotungstic acid volumetric method.

因此,亟待建立一种适用于两性离子磺化酚醛树脂阳离子度的测定方法。Therefore, it is urgent to establish a method suitable for the determination of the cationic degree of zwitterionic sulfonated phenolic resin.

发明内容Contents of the invention

为了克服现有技术的缺陷,本发明的目的是提供一种检测结果准确,操作过程易于控制的两性离子磺化酚醛树脂阳离子度的测定方法。In order to overcome the defects of the prior art, the object of the present invention is to provide a method for measuring the cationicity of zwitterionic sulfonated phenolic resin with accurate detection results and easy control of the operation process.

为了实现以上目的,本发明所采用的技术方案是:In order to achieve the above object, the technical solution adopted in the present invention is:

一种两性离子磺化酚醛树脂阳离子度的测定方法,包括以下操作步骤:A method for measuring the cationic degree of zwitterionic sulfonated phenolic resin, comprising the following steps:

1)测定每0.5g纯净的两性离子磺化酚醛树脂在硅藻土中的吸附量m1) Measure the adsorption capacity m of every 0.5g of pure zwitterionic sulfonated phenolic resin in diatomite;

2)带入公式A=863.87m-24.54,计算得出两性离子磺化酚醛树脂的阳离子度A。2) Enter the formula A=863.87m to absorb -24.54 to calculate the cationic degree A of the zwitterionic sulfonated phenolic resin.

进一步的,步骤1)中每0.5g纯净的两性离子磺化酚醛树脂在硅藻土中的吸附量m的具体测定方法的操作步骤为:Further, in step 1), the operation steps of the specific determination method of the adsorption capacity m of every 0.5 g of pure zwitterionic sulfonated phenolic resin in diatomite are as follows:

a:取0.5g纯净的两性离子磺化酚醛树脂加入水中溶解,得树脂溶液;之后取质量为m3的硅藻土加入树脂溶液中,混合均匀,密封,振荡,得固液混合溶液;a: Take 0.5 g of pure zwitterionic sulfonated phenolic resin and dissolve it in water to obtain a resin solution; then take diatomaceous earth with a mass of m3 and add it to the resin solution, mix evenly, seal, and oscillate to obtain a solid-liquid mixed solution;

b:取质量为m4的滤纸,采用该滤纸将步骤a制备的固液混合溶液进行固液分离,分离完毕后采用滤纸包覆分离的固体进行干燥后,冷却至室温称其重量为m5,计算吸附量m=m5-m3-m4b: Take a filter paper with a mass of m 4 , use the filter paper to separate the solid-liquid mixed solution prepared in step a, after the separation is completed, use the filter paper to cover the separated solid and dry it, then cool it to room temperature and weigh it as m 5 , calculate the adsorption capacity m absorption = m 5 -m 3 -m 4 .

由于在硅藻土吸附两性离子磺化酚醛树脂的过程中,硅藻土和两性离子磺化酚醛树脂的用量比例,影响两者之间的吸附性能。经试验研究,两性离子磺化酚醛树脂在1g硅藻土表面的饱和吸附量为41mg/g,随着吸附剂硅藻土加量增加,两性离子磺化酚醛树脂在硅藻土上的吸附质量呈下降趋势,为了使两性离子磺化酚醛树脂充分吸附在硅藻土上,优选的,所述硅藻土的质量m3为2.0g。During the process of diatomite adsorbing zwitterionic sulfonated phenolic resin, the ratio of the amount of diatomite and zwitterionic sulfonated phenolic resin affects the adsorption performance between the two. According to experimental research, the saturated adsorption capacity of zwitterionic sulfonated phenolic resin on the surface of 1g diatomite is 41mg/g. In order to make the zwitterionic sulfonated phenolic resin fully adsorb on the diatomite, preferably, the mass m3 of the diatomite is 2.0 g.

为了进一步促进两性离子磺化酚醛树脂与硅藻土之间的完全吸附过程,优选的,步骤a所述振荡的振荡转速为150r/min~200r/min,振荡温度为30~35℃,振荡时间为60~120min。In order to further promote the complete adsorption process between the zwitterionic sulfonated phenolic resin and diatomite, preferably, the oscillation speed of the oscillation described in step a is 150r/min~200r/min, the oscillation temperature is 30~35°C, and the oscillation time 60~120min.

进一步的,步骤b中所述固液分离的具体方法为:采用滤纸对步骤a制备的固液混合溶液进行过滤,用干净的容器收集过滤液,并用收集的过滤液冲洗盛装固液混合溶液的容器,将冲洗后的过滤液重新经过滤纸进行过滤,重复操作至盛装固液混合溶液的容器冲洗干净,即完成。Further, the specific method of solid-liquid separation described in step b is: use filter paper to filter the solid-liquid mixed solution prepared in step a, collect the filtrate in a clean container, and use the collected filtrate to rinse the container containing the solid-liquid mixed solution. Container, filter the rinsed filtrate through filter paper again, and repeat the operation until the container containing the solid-liquid mixed solution is rinsed clean, which is completed.

进一步的,步骤b中所述干燥为在105±3℃温度下烘干2h~4h。Further, the drying in step b is drying at a temperature of 105±3° C. for 2 hours to 4 hours.

进一步的,还包括首先取待测两性离子磺化酚醛树脂进行纯化制得纯净的两性离子磺化酚醛树脂,具体操作步骤为:Further, it also includes firstly taking the zwitterionic sulfonated phenolic resin to be tested and purifying to obtain a pure zwitterionic sulfonated phenolic resin. The specific operation steps are:

A:取待测两性离子磺化酚醛树脂分散在乙醇溶液中,静置20~40min后,进行固液分离,收集固体,并对收集的固体依次进行洗涤、干燥后,制备半纯品;A: Take the zwitterionic sulfonated phenolic resin to be tested and disperse it in the ethanol solution, let it stand for 20-40 minutes, then separate the solid from the liquid, collect the solid, and wash and dry the collected solid in turn to prepare a semi-pure product;

B:取步骤1)制备的半纯品溶解在水中,得半纯品溶液;之后将半纯品溶液离心固液分离,收集上清液,得溶解有纯净两性离子磺化酚醛树脂的溶液。B: Dissolve the semi-pure product prepared in step 1) in water to obtain a semi-pure product solution; then centrifuge the semi-pure product solution for solid-liquid separation, collect the supernatant, and obtain a solution in which pure zwitterionic sulfonated phenolic resin is dissolved.

进一步的,步骤B中离心固液分离的具体方法为:取半纯品溶液用离心机以2000~3000r/min转速离心15~20min,将上清液移入洁净容器中,用水洗涤盛装半成品溶液的容器,并收集洗涤液,再次进行离心沉降,重复上述操作四次,收集全部的上清液,即完成。Further, the specific method of centrifuging solid-liquid separation in step B is: take the semi-pure solution and centrifuge it with a centrifuge at a speed of 2000-3000r/min for 15-20min, move the supernatant into a clean container, and wash the semi-pure solution with water. container, and collect the washing liquid, and perform centrifugal sedimentation again, repeat the above operation four times, and collect all the supernatant, which is completed.

进一步的,步骤A中所述干燥为在50±3℃温度下干燥4h~5h。Further, the drying in step A is drying at a temperature of 50±3°C for 4h~5h.

进一步的,步骤A中采用乙醇溶液对收集的固体进行洗涤,所述乙醇溶液的质量浓度为90%~95%。Further, in step A, the collected solid is washed with ethanol solution, and the mass concentration of the ethanol solution is 90%-95%.

进一步的,上述硅藻土和滤纸均为105±3℃条件下烘干至恒重的硅藻土和滤纸,其中滤纸为定量慢速滤纸。Further, the above-mentioned diatomite and filter paper are all diatomite and filter paper dried at 105±3° C. to constant weight, wherein the filter paper is quantitative slow-speed filter paper.

为了准确获取0.5g纯净的两性离子磺化酚醛树脂,还包括测定待测两性离子磺化酚醛树脂的水不溶物含量,具体测定方法为:取质量为m1的待测两性离子磺化酚醛树脂溶解于水中,沸水浴加热1h后,进行离心充分固液分离,收集固相沉降物,105±2℃条件下烘干4h后进行冷却,称取其质量为m2,则待测两性离子磺化酚醛树脂的水不溶物质量百分含量为B= m2/ m1×100%。利用测定的水不溶物质量百分含量B,在上述步骤B中称取步骤1)制备的半纯品质量m6,那么该半纯品中纯净两性离子磺化酚醛树脂的质量m7= m6-m6×B,即步骤B中制成的溶解有纯净两性离子磺化酚醛树脂中含有的纯净两性离子磺化酚醛树脂的质量为m7,则可根据实际测量过程中所需的0.5g纯净两性离子磺化酚醛树脂,按照比例取步骤B制成的溶解有纯净两性离子磺化酚醛树脂的溶液。In order to accurately obtain 0.5 g of pure zwitterionic sulfonated phenolic resin, it also includes determining the water-insoluble content of the zwitterionic sulfonated phenolic resin to be tested. Dissolve in water, heat in a boiling water bath for 1 hour, centrifuge for sufficient solid-liquid separation, collect solid-phase sediment, dry at 105±2°C for 4 hours, then cool, weigh its mass as m 2 , then the zwitterion sulfonium to be tested The mass percentage of water-insoluble matter in the phenolic resin is B= m 2 /m 1 ×100%. Using the measured water-insoluble mass percentage B, weigh the mass m 6 of the semi-pure product prepared in step 1) in the above step B, then the mass m 7 of the pure zwitterionic sulfonated phenolic resin in the semi-pure product = m 6 -m 6 ×B, that is, the mass of the pure zwitterionic sulfonated phenolic resin dissolved in the pure zwitterionic sulfonated phenolic resin prepared in step B is m 7 , it can be calculated according to the 0.5 required in the actual measurement process g pure zwitterionic sulfonated phenolic resin, take the solution prepared in step B dissolved with pure zwitterionic sulfonated phenolic resin according to the ratio.

本发明两性离子磺化酚醛树脂阳离子度的测定方法,根据两性离子磺化酚醛树脂分子链上的阳离子季铵盐基团具有良好的吸附性能,利用硅藻土作为标准吸附介质(吸附剂)对0.5g的两性离子磺化酚醛树脂吸附前后质量的变化计算吸附质量,不同阳离子度的两性离子磺化酚醛树脂对应不同的吸附质量,再带入本发明总结出的0.5g两性离子磺化酚醛树脂吸附量与阳离子度之间的关系式,计算得出实际所测两性离子磺化酚醛树脂的阳离子度。本发明这种基于吸附称重法的阳离子度测定方法,避免了现有技术中阴离子对测定过程和测定结果的影响,提高检测结果的准确性,并且具有广泛的适用性和较强的可操作性,而且仪器设备条件要求低,能在常规检测实验室推广应用。The method for measuring the cationic degree of the zwitterionic sulfonated phenolic resin of the present invention is based on the fact that the cationic quaternary ammonium salt group on the molecular chain of the zwitterionic sulfonated phenolic resin has good adsorption properties, and diatomaceous earth is used as a standard adsorption medium (adsorbent) for The mass change of 0.5g zwitterionic sulfonated phenolic resin before and after adsorption is used to calculate the adsorption mass, and the zwitterionic sulfonated phenolic resins with different cationic degrees correspond to different adsorption masses, and then brought into the 0.5g zwitterionic sulfonated phenolic resin summarized in the present invention The relationship between the adsorption amount and the cationic degree can be calculated to obtain the cationic degree of the actually measured zwitterionic sulfonated phenolic resin. The cationic degree determination method based on the adsorption weighing method of the present invention avoids the influence of anions on the determination process and measurement results in the prior art, improves the accuracy of the detection results, and has wide applicability and strong operability It is unique and has low requirements for equipment and equipment, so it can be popularized and applied in routine testing laboratories.

进一步的,本发明测定方法对待测两性离子磺化酚醛树脂进行提纯和去除在职,排出干扰因素,得到纯净的两性离子磺化酚醛树脂,进一步提高检测结果的准确性。Furthermore, the determination method of the present invention purifies and removes the zwitterionic sulfonated phenolic resin to be tested, removes the interference factors, and obtains the pure zwitterionic sulfonated phenolic resin, further improving the accuracy of the detection result.

附图说明Description of drawings

图1为实施例两性离子磺化酚醛树脂的吸附量与阳离子度的线性回归曲线。Fig. 1 is the linear regression curve of the adsorption amount and cationic degree of zwitterionic sulfonated phenolic resin of embodiment.

具体实施方式Detailed ways

下面通过具体实施例对本发明的技术方案进行详细说明。The technical solution of the present invention will be described in detail below through specific examples.

实施例Example

本实施例两性离子磺化酚醛树脂阳离子度的测定方法,具体操作步骤为:The assay method of the cationic degree of zwitterionic sulfonated phenolic resin in this embodiment, the specific operation steps are:

1)测定0.5g纯净两性离子磺化酚醛树脂在硅藻土中的吸附量m1) Determination of the adsorption capacity m of 0.5g of pure zwitterionic sulfonated phenolic resin in diatomite;

A:测定水不溶物的质量百分含量:A: Determination of the mass percentage of water-insoluble matter:

a:取待测样品试样质量m1为1.0004g(称准至0.0001g),置于150mL烧杯中,加入100mL蒸馏水搅匀,在沸水浴中加热1h,得待测样品水溶液;a: Take the sample mass m1 of the sample to be tested as 1.0004g (accurate to 0.0001g), put it in a 150mL beaker, add 100mL of distilled water, stir well, heat in a boiling water bath for 1h, and obtain the aqueous solution of the sample to be tested;

b:分两次把步骤a制备的待测样品水溶液移入预先在105±2℃烘干至恒重的6支离心试管内,其中记录6支离心管的空管质量为m8,将上述6支离心管放入转速为3000r/min的离心机中离心沉降20min,取出离子管,用吸管将上部清夜吸出弃去;b: Transfer the aqueous solution of the sample to be tested prepared in step a into 6 centrifuge tubes that have been dried at 105±2°C to constant weight twice, and record the mass of the empty tubes of the 6 centrifuge tubes as m 8 . Place the centrifuge tube in a centrifuge with a rotating speed of 3000r/min for 20 minutes, take out the ion tube, suck out the upper clear part with a straw and discard it;

c:用100mL蒸馏水洗涤烧杯中剩余物4次,并移入离心管,离心沉降,取出离心管,用吸管将上部清夜吸出弃去;c: Wash the residue in the beaker with 100mL distilled water for 4 times, transfer it to a centrifuge tube, settle by centrifugation, take out the centrifuge tube, suck out the upper clear part with a straw and discard;

d:把离心管倾斜于另一清洁恒重的烧杯中,于105±2℃烘箱中烘4h,移入干燥器,冷却至室温(不得少于30min),称量离心管的重量为m9,则试样中不溶物的质量m2= m9- m8d: Tilt the centrifuge tube into another clean beaker with constant weight, bake it in an oven at 105±2°C for 4 hours, move it into a desiccator, cool it to room temperature (not less than 30min), weigh the centrifuge tube as m 9 , Then the mass m 2 of the insoluble matter in the sample = m 9 - m 8 ;

e:计算待测样品两性离子磺化酚醛树脂的水不溶物质量分数B按下式计算:e: Calculate the water-insoluble mass fraction B of the zwitterionic sulfonated phenolic resin of the sample to be tested according to the following formula:

B:样品提纯B: Sample purification

a:称取质量m10为2.05 g的试样,置于250 mL烧杯中,用玻璃棒一边缓慢搅动,一边加入100ml质量浓度为90%~95%的乙醇溶液,使样品均匀分散在乙醇溶液中,静置30min。a: Weigh a sample with a mass m 10 of 2.05 g, place it in a 250 mL beaker, and slowly stir it with a glass rod, while adding 100 ml of ethanol solution with a mass concentration of 90%~95%, so that the sample is evenly dispersed in the ethanol solution , let stand for 30min.

b:用烘干至恒重的单层中速定性滤纸过滤,过滤完毕后,再用相同浓度的30ml乙醇分三次洗涤滤纸表面的样品,清除样品表面的残余杂质;b: Filter with a single layer of medium-speed qualitative filter paper dried to constant weight. After the filter is completed, wash the sample on the surface of the filter paper three times with 30ml of ethanol of the same concentration to remove the residual impurities on the surface of the sample;

c:将折叠包有样品的滤纸放于恒温干燥箱中,在50±3℃温度下烘干4~5小时,再将包有样品的滤纸立即放于干燥器内,冷却至室温,得半纯品;c: Put the folded filter paper wrapped with the sample in a constant temperature drying oven, and dry it at 50±3°C for 4~5 hours, then immediately put the filter paper wrapped with the sample in the desiccator, cool to room temperature, and obtain half Pure;

C:去除水不溶物C: remove water insoluble matter

a:称取质量m6为1.3242g半纯品,置于干燥洁净的250 mL烧杯中,加入100 mL蒸馏水,在磁力搅拌器上以400r/min~500r/min低速搅拌,使其充分溶解,得半纯品溶液;a: Weigh 1.3242g of semi-pure product with mass m6 , put it in a dry and clean 250 mL beaker, add 100 mL of distilled water, and stir at a low speed of 400r/min~500r/min on a magnetic stirrer to fully dissolve it. A semi-pure solution is obtained;

b:将上述半纯品溶液用离心机以2500r/min转速离心18min,用吸管将上部溶液小心移入洁净的250mL容量瓶中,用100mL蒸馏水反复洗涤烧杯中剩余物4次,并移入离心管,离心沉降,用吸管将上部清液转移至上述容量瓶中,并定容至250ml,即得溶解有纯净两性离子磺化酚醛树脂的溶液;该溶液中纯净两性离子磺化酚醛树脂的含量m7=m6×(1-B)=1.3242×0.944=1.25g;b: Use a centrifuge to centrifuge the above semi-pure product solution at 2500r/min for 18min, carefully transfer the upper solution into a clean 250mL volumetric flask with a straw, wash the residue in the beaker with 100mL distilled water repeatedly 4 times, and transfer it to a centrifuge tube. Settling by centrifugation, transfer the supernatant liquid to the above-mentioned volumetric flask with a straw, and set the volume to 250ml to obtain a solution in which pure zwitterionic sulfonated phenolic resin is dissolved; the content of pure zwitterionic sulfonated phenolic resin in the solution is m 7 =m 6 ×(1-B)=1.3242×0.944=1.25g;

D:吸附称重法测定吸附量D: Determination of adsorption capacity by adsorption weighing method

a:用100ml移液管准确移取100ml上述溶解有纯净两性离子磺化酚醛树脂的溶液,置于干燥洁净的250mL锥形瓶中;用称量纸称取质量m3为2.0002g,在105±3 ℃烘干至恒重的硅藻土,倒入上述锥形瓶中,将固液混合摇匀,用保鲜膜密封瓶口,将锥形瓶放置于恒温双功能振荡器中振荡120min,振荡方式为回旋式,振荡温度为32℃,振荡转速为180r/min;a: Use a 100ml pipette to accurately pipette 100ml of the above-mentioned solution dissolved in pure zwitterionic sulfonated phenolic resin, and place it in a dry and clean 250mL conical flask; use weighing paper to weigh the mass m3 to 2.0002g, Diatomite dried at ±3°C to constant weight, poured into the above-mentioned Erlenmeyer flask, mixed the solid and liquid, sealed the mouth of the bottle with plastic wrap, and placed the Erlenmeyer flask in a constant temperature dual-function oscillator to shake for 120min. The oscillation mode is rotary, the oscillation temperature is 32°C, and the oscillation speed is 180r/min;

b:振荡结束后,先将干燥洁净的漏斗置于漏斗架上,漏斗内放入单层烘干至恒重并已知质量m4为1.9867g的滤纸,再将锥形瓶内的固液混合体缓慢倒入滤纸内,漏斗下方用干燥洁净的100mL烧杯收集滤液,同时用收集的滤液冲洗锥形瓶内壁粘附的固体颗粒,并将滤液再次倒入滤纸内,反复4次,直至将锥形瓶内壁的固体颗粒冲洗干净;b: After the oscillation is over, put the dry and clean funnel on the funnel holder first, put a single layer of filter paper in the funnel that has been dried to constant weight and has a known mass m4 of 1.9867g, and then put the solid-liquid in the Erlenmeyer flask Slowly pour the mixture into the filter paper, collect the filtrate with a dry and clean 100mL beaker under the funnel, and at the same time use the collected filtrate to wash the solid particles adhered to the inner wall of the Erlenmeyer flask, and pour the filtrate into the filter paper again, repeating 4 times until the The solid particles on the inner wall of the Erlenmeyer flask are washed away;

c:待滤液过滤完毕,将折叠包有硅藻土的滤纸放于干燥洁净的称量瓶中,于105℃±3℃下烘干2h;烘干完毕,将包有硅藻土的滤纸立即放于干燥器内,冷却20min后称重质量m5为4.0241g;c: After the filtrate is filtered, put the folded filter paper wrapped with diatomaceous earth in a dry and clean weighing bottle, and dry it at 105°C±3°C for 2 hours; after drying, put the filter paper wrapped with diatomaceous earth immediately Put it in a desiccator, and after cooling for 20 minutes, weigh the mass m5 to be 4.0241g;

d:计算吸附量m= m5-m3-m4=4.0241g-1.9867g-2.0002g=0.0372gd: Calculation of adsorption m absorption = m 5 -m 3 -m 4 =4.0241g-1.9867g-2.0002g=0.0372g

2)计算阳离子度:将步骤1)中计算的吸附量m,带入公式A=863.87×m-24.54,计算得阳离子度A=863.87×0.0372-24.54=7.6%。2) Calculation of cationic degree: Put the adsorption amount mab calculated in step 1) into the formula A=863.87× mab -24.54, and calculate the cationic degree A=863.87×0.0372-24.54=7.6%.

其中公式A=863.87×m-24.54由以下方法获得:按照上述步骤1)的方式分别测定实验室测定出经过元素分析法确定阳离子度分别为2.10%、4.04%、6.38%、8.46%、11.02%、13.34%和15.12%的两性离子磺化酚醛树脂的吸附质量,经数学回归分析得到阳离子度与吸附质量的线性回归方程曲线,如图1所示,即得阳离子度与吸附质量之间的关系式为 A =863.87m-24.54,R2=0.9978。The formula A=863.87×m-24.54 is obtained by the following method: According to the method of the above step 1), the laboratory determined that the cationic degree was determined to be 2.10%, 4.04%, 6.38%, 8.46%, and 11.02 respectively by elemental analysis. %, 13.34% and 15.12% of the adsorption mass of zwitterionic sulfonated phenolic resin, the linear regression equation curve of cationic degree and adsorption mass is obtained through mathematical regression analysis, as shown in Figure 1, that is, the relationship between cationic degree and adsorption mass The relational formula is A =863.87m suction -24.54, R 2 =0.9978.

对比例1Comparative example 1

本对比例为四苯硼钠重量法测定实施例所测的两性离子磺化酚醛树脂的阳离子度,具体操作步骤为:This comparative example is the cationic degree of the zwitterionic sulfonated phenolic resin measured by the sodium tetraphenyl borate gravimetric method, and the specific operation steps are:

1)按照上述实施例中步骤A、步骤B和步骤C同样的方法制得溶解有纯净两性离子磺化酚醛树脂的溶液;1) Prepare a solution in which pure zwitterionic sulfonated phenolic resin is dissolved in the same manner as step A, step B and step C in the above examples;

2)测定阳离子度:2) Determination of cationic degree:

a:用100mL移液管准确移取100ml上述溶解有纯净两性离子磺化酚醛树脂的溶液,于200mL烧杯中,加入2~3滴酚酞指示剂,将溶液用1 0%氢氧化钠调至显红色.加8 mL甲醛溶液,此时若红色消失,应再加几滴氢氧化钠调至红色。盖上表面皿,将溶液于沸水浴上加热10min.此时溶液保持红色不褪。取下烧杯稍冷,在搅拌下逐滴加入10mL四苯硼钠标准溶液,继续搅拌1 min,迅速冷却到20℃以下,放置10min;a: Use a 100mL pipette to accurately pipette 100ml of the above-mentioned solution dissolved in pure zwitterionic sulfonated phenolic resin, add 2~3 drops of phenolphthalein indicator to a 200mL beaker, and adjust the solution with 10% sodium hydroxide to a clear red. Add 8 mL of formaldehyde solution, if the red color disappears at this time, add a few drops of sodium hydroxide to adjust to red color. Cover with a watch glass, and heat the solution on a boiling water bath for 10 min. At this point the solution remains red. Remove the beaker and cool slightly, add 10mL sodium tetraphenylborate standard solution drop by drop under stirring, continue to stir for 1 min, cool rapidly to below 20°C, and place for 10 min;

b:用预先在120℃±2℃下干燥至恒重的4号玻璃砂芯坩埚抽滤,先抽滤上层清液,再用洗涤液转移沉淀至坩埚中,继续用洗涤液洗涤沉淀10次,。每次洗涤液用量约5mL,将坩埚于120℃±2℃烘干至恒重,测定其重量为m10b: Suction filtration with the No. 4 glass sand core crucible which was pre-dried at 120°C±2°C to constant weight, first suction filter the supernatant liquid, then transfer the precipitate to the crucible with the washing liquid, and continue to wash the precipitate 10 times with the washing liquid ,. The amount of each washing liquid is about 5mL, and the crucible is dried at 120℃±2℃ to constant weight, and its weight is measured as m 10 .

c:计算阳离子度:阳离子度A(%)=m10/m×0 .4845×100%c: Calculation of cationic degree: cationic degree A(%)=m 10 /m×0.4845×100%

式中:In the formula:

m10--烘干后四苯硼化铵的质量,g:m 10 -- the mass of tetraphenylammonium boride after drying, g:

m--100ml溶解有纯净两性离子磺化酚醛树脂的溶液中含有的纯净两性离子磺化酚醛树脂的质量,g:m - the mass of pure zwitterionic sulfonated phenolic resin contained in a solution of pure zwitterionic sulfonated phenolic resin dissolved in 100ml, g:

0.4845--四苯硼化铵换算为季铵盐的系数。0.4845--The conversion coefficient of ammonium tetraphenyl boride to quaternary ammonium salt.

阳离子度A=0.0477/0.5000×0 .484 5×100%=4.62%Cationic degree A=0.0477/0.5000×0.484 5×100%=4.62%

对比例2Comparative example 2

本对比例为磷钨酸滴定法测定实施例所测的两性离子磺化酚醛树脂的阳离子度,具体操作步骤为:This comparative example is the cationic degree of the zwitterionic sulfonated phenolic resin measured by the phosphotungstic acid titration method, and the specific operation steps are:

1)按照上述实施例中步骤A、步骤B和步骤C同样的方法制得溶解有纯净两性离子磺化酚醛树脂的溶液;1) Prepare a solution in which pure zwitterionic sulfonated phenolic resin is dissolved in the same manner as step A, step B and step C in the above examples;

2)测定阳离子度:2) Determination of cationic degree:

a:把阳离子交换树脂处理成钠型,把准确移取上述含有1.100g纯净两性离子磺化酚醛树脂的溶液过已处理好的阳离子交换树脂,用蒸馏水洗涤至无色后,用 60℃~70℃的 20%的氯化钠80mL 以5 mL/min~6 mL/min 的速度洗脱树脂,洗脱液用 1mol/L 盐酸调至pH值为 3~4,收集洗脱流出液;a: Treat the cation exchange resin into sodium form, accurately pipette the above-mentioned solution containing 1.100g of pure zwitterionic sulfonated phenolic resin through the treated cation exchange resin, wash with distilled water until it is colorless, and wash it with 60 ℃ ~ 70 80mL of 20% sodium chloride at ℃ to elute the resin at a rate of 5 mL/min to 6 mL/min, the eluent is adjusted to a pH value of 3 to 4 with 1mol/L hydrochloric acid, and the elution effluent is collected;

b:往上述收集的洗脱流出液中加 6 滴~8 滴刚果红指示剂,用磷钨酸标准溶液滴定,生成沉淀后(无沉淀生成,说明试样无阳离子),缓慢滴定至红色完全消失,溶液为纯蓝色为终点。b: Add 6-8 drops of Congo red indicator to the elution effluent collected above, titrate with phosphotungstic acid standard solution, after precipitation is formed (no precipitation, indicating that the sample has no cations), slowly titrate until the red color is completely disappeared, and the solution was pure blue as the end point.

c:计算:阳离子度A(%)=(10-3CV/m)×2880×100%c: Calculation: cationic degree A(%)=(10 -3 CV/m)×2880×100%

C——磷钨酸摩尔浓度,单位为摩尔每升(mol/L);C——molar concentration of phosphotungstic acid, in moles per liter (mol/L);

V ——消耗磷钨酸体积,单位为毫升(mL);V - the volume of phosphotungstic acid consumed, in milliliters (mL);

m——试样质量,单位为克(g);m——sample mass, in grams (g);

2880——磷钨酸的摩尔质量,g/mol。2880——Molar mass of phosphotungstic acid, g/mol.

阳离子度A=(10-3×0.0206×0.700/1.100)×2880×100%=3.8%Cationic degree A = (10 -3 × 0.0206 × 0.700/1.100) × 2880 × 100% = 3.8%

试验例1Test example 1

比较实施例、对比例1和对比例2对同样的两性磺化酚醛树脂的阳离子度的测定结果大小,结果显示实施例>对比例1>对比例2,由该结果可知由于受到阴离子和认为操作中存在判断误差影响,使得对于阳离子度的测定结果偏低,而实施例所述的方法克服了上述缺陷,提高了对于阳离子度的测定结果的准确性。Comparative example, comparative example 1 and comparative example 2 are to the measurement result size of the cationic degree of same amphoteric sulfonated phenolic resin, and the result shows embodiment > comparative example 1 > comparative example 2, by this result we can know that due to being subjected to anion and thinking operation Influenced by judgment error, the result of the determination of the cationic degree is low, but the method described in the embodiment overcomes the above-mentioned defects and improves the accuracy of the measured result of the cationic degree.

试验例2 准确性验证试验Test Example 2 Accuracy Verification Test

试验方法:将实验室合成的4个不同阳离子度两性离子磺化酚醛树脂样品经醇洗处理后,采用原子吸收光谱进行氮元素分析和本发明实施例提供的测定方法进行相同样品的阳离子度测定,结果对比如下表1所示:Test method: 4 amphoteric ion sulfonated phenolic resin samples with different cationic degrees synthesized in the laboratory were washed with alcohol, and the nitrogen element analysis was carried out by atomic absorption spectroscopy and the cationic degree of the same sample was measured by the measurement method provided in the embodiment of the present invention. , and the results are compared as shown in Table 1 below:

样品编号Sample serial number 11 22 33 44 元素分析法Elemental Analysis 2.05%2.05% 5.105.10 6.426.42 12.4512.45 实施例所述方法The method described in the embodiment 2.00%2.00% 5.045.04 6.366.36 12.4012.40 标准偏差standard deviation 2.40%2.40% 1.20%1.20% 0.93%0.93% 0.40%0.40%

结论:本发明提供的吸附称重法测定两性离子磺化酚醛树脂的阳离子度与元素分析法得到的阳离子度测定值大小基本吻合,四个样品的相对误差均小于2.5%。由此可见,本发明提供的吸附称重法测定两性离子磺化酚醛树脂阳离子度是准确和可靠的。Conclusion: The cationic degree of zwitterionic sulfonated phenolic resin determined by the adsorption weighing method provided by the present invention is basically consistent with the measured value of the cationic degree obtained by the elemental analysis method, and the relative errors of the four samples are all less than 2.5%. It can be seen that the adsorption weighing method provided by the present invention is accurate and reliable for determining the cationic degree of the zwitterionic sulfonated phenolic resin.

Claims (10)

1. a kind of assay method of amphion sulfonated phenol formaldehyde resin cationic degree, it is characterised in that including following operating procedure:
1)Measure is per adsorbance m of the amphion sulfonated phenol formaldehyde resin pure 0.5g in diatomiteInhale
2)Bring formula A=863.87m intoInhale- 24.54, the cationic degree A of amphion sulfonated phenol formaldehyde resin is calculated.
2. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 1, it is characterised in that step 1)In per adsorbance m of the amphion sulfonated phenol formaldehyde resin pure 0.5g in diatomiteInhaleSpecific assay method operation Step is:
a:The amphion sulfonated phenol formaldehyde resin for taking 0.5g pure is added to the water dissolving, obtains resin solution;It is m to take quality afterwards3's Diatomite is added in resin solution, is well mixed, and is sealed, and vibration, obtains solid-liquid mixed solution;
b:It is m to take quality4Filter paper, the solid-liquid mixed solution for being prepared step a using the filter paper carried out separation of solid and liquid, separated After being dried after finishing using the solid of filter paper cladding separation, it is referred to as m to be cooled to room temperature its weight5, calculate adsorbance mInhale=m5- m3-m4
3. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 2, it is characterised in that described Diatomaceous quality m3For 2.0g.
4. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 2, it is characterised in that step The vibration rotating speed vibrated described in a is 150r/min ~ 200r/min, and vibration temperature is 30 ~ 35 DEG C, and duration of oscillation is 60 ~ 120min.
5. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 2, it is characterised in that step The specific method of separation of solid and liquid described in b is:Solid-liquid mixed solution prepared by step a is filtered using filter paper, with clean Container collection filtered fluid, and with collect filtered fluid rinse contain solid-liquid mixed solution container, by the filtered fluid after flushing Again filtered by filter paper, repeat to the container for containing solid-liquid mixed solution and rinse well, that is, complete.
6. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 2, it is characterised in that step Dried described in b is that 2h ~ 4h is dried at a temperature of 105 ± 3 DEG C.
7. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 1, it is characterised in that also wrap Include and take amphion sulfonated phenol formaldehyde resin to be measured to carry out the amphion sulfonated phenol formaldehyde resin that purifying is made pure, specific behaviour first It is as step:
A:Take amphion sulfonated phenol formaldehyde resin to be measured to be dispersed in ethanol solution, after standing 20 ~ 40min, carry out separation of solid and liquid, Solid is collected, and the solid of collection is washed, after drying successively, prepares half sterling;
B:Take step 1)Half sterling prepared is dissolved in water, and obtains half sterling solution;Afterwards by half sterling solution centrifugal solid-liquid point From, collect supernatant, obtain the solution dissolved with pure amphion sulfonated phenol formaldehyde resin.
8. the assay method of amphion sulfonated phenol formaldehyde resin cationic degree as claimed in claim 7, it is characterised in that step The specific method of centrifugal solid-liquid separation is in B:Take half sterling solution centrifuge with 2000 ~ 3000r/min rotating speeds centrifugation 15 ~ 20min, supernatant is moved into clean container, the container for containing semi-finished product solution is washed with water, and collect cleaning solution, entered again Row centrifugal sedimentation, repeats aforesaid operations four times, collects whole supernatants, that is, completes.
9. the assay method of amphion sulfonated phenol formaldehyde resin ion degree as claimed in claim 7, it is characterised in that step A Described in dry be at a temperature of 50 ± 3 DEG C dry 4h ~ 5h.
10. the assay method of which resin ion degree is removed in amphion sulfonation as claimed in claim 7 point, it is characterised in that step The solid of collection is washed using ethanol solution in rapid A, the mass concentration of the ethanol solution is 90% ~ 95%.
CN201610858002.3A 2016-09-28 2016-09-28 A kind of determination method of cationic degree of zwitterion sulfonated phenolic resin Active CN107870136B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610858002.3A CN107870136B (en) 2016-09-28 2016-09-28 A kind of determination method of cationic degree of zwitterion sulfonated phenolic resin

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610858002.3A CN107870136B (en) 2016-09-28 2016-09-28 A kind of determination method of cationic degree of zwitterion sulfonated phenolic resin

Publications (2)

Publication Number Publication Date
CN107870136A true CN107870136A (en) 2018-04-03
CN107870136B CN107870136B (en) 2020-02-21

Family

ID=61761160

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610858002.3A Active CN107870136B (en) 2016-09-28 2016-09-28 A kind of determination method of cationic degree of zwitterion sulfonated phenolic resin

Country Status (1)

Country Link
CN (1) CN107870136B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08259609A (en) * 1995-03-27 1996-10-08 Kuraray Co Ltd Dispersion stabilizer for suspension polymerization of vinyl compounds
US20080003192A1 (en) * 2006-06-29 2008-01-03 Modi Jashawant J Functional compositions containing cationic hydrophobically modified polysaccharides for personal care, household & institutional and pet care products
CN101871873A (en) * 2010-06-11 2010-10-27 东华大学 A heavy metal ion detection device and preparation method thereof
CN104677771A (en) * 2015-03-26 2015-06-03 成都理工大学 Magnetic levitation weight method-based method for determining porosity of shale
CN105548049A (en) * 2015-12-29 2016-05-04 中核北方核燃料元件有限公司 Method for measuring content of chlorine in phenolic resin

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08259609A (en) * 1995-03-27 1996-10-08 Kuraray Co Ltd Dispersion stabilizer for suspension polymerization of vinyl compounds
US20080003192A1 (en) * 2006-06-29 2008-01-03 Modi Jashawant J Functional compositions containing cationic hydrophobically modified polysaccharides for personal care, household & institutional and pet care products
CN101871873A (en) * 2010-06-11 2010-10-27 东华大学 A heavy metal ion detection device and preparation method thereof
CN104677771A (en) * 2015-03-26 2015-06-03 成都理工大学 Magnetic levitation weight method-based method for determining porosity of shale
CN105548049A (en) * 2015-12-29 2016-05-04 中核北方核燃料元件有限公司 Method for measuring content of chlorine in phenolic resin

Non-Patent Citations (9)

* Cited by examiner, † Cited by third party
Title
A.R. AL-HASHMI ET AL.: "The role of hydration degree of cations and anions on the adsorption of high-molecular-weight nonionic polyacrylamide on glass surfaces", 《COLLOIDS AND SURFACES A: PHYSICOCHEMICAL AND ENGINEERING ASPECTS》 *
GULAY BAYRAMOGLU ET AL.: "Adsorption kinetics and thermodynamic parameters of cationic dyes from aqueous solutions by using a new strong cation-exchange resin", 《CHEMICAL ENGINEERING JOURNAL》 *
HIROO TANAKA ET AL.: "Adsorption of cationic polyacrylamides onto monodisperse polystyrene latices and cellulose fiber_ Effect of molecular weight and charge density of cationic polyacrylamides", 《JOURNAL OF COLLOID AND INTERFACE SCIENCE》 *
TOM LINDSTKOM: "Adsorption of Cationic Polyacrylamides on Cellulose", 《JOURNAL OF COLLOID AND INTERFACE SCIENCE》 *
杜灿敏 等: "钻井液用大阳离子中阳离子度的测定方法初探", 《石油工业技术监督》 *
沈丽萍 等: "阳离子磺甲基酚醛树脂阳离子度的测定", 《理化检验-化学分册》 *
郑怀礼 等: "阳离子聚丙烯酰胺P(AM-DAC)阳离子度的测定", 《重庆大学学报》 *
雷祖猛 等: "钻井液用阳离子烷基糖苷阳离子度的测定", 《能源化工》 *
黄伟琴 等: "钻井液用阳离子磺甲基酚醛树脂阳离子度的测定方法初探", 《中国石油和化工标准与质量》 *

Also Published As

Publication number Publication date
CN107870136B (en) 2020-02-21

Similar Documents

Publication Publication Date Title
Marhol Ion Exchangers in Analytical Chemistry. Their Properties and Use in Inorganic Chemistry: Ion Exchangers in Analytical Chemistry. Their Properties and Use in Inorganic Chemistry
CN108084453A (en) The aperture expanding method of UiO-66 metal-organic framework materials and application
CN105921103B (en) A kind of while fixed nitrogen phosphorus La (OH)3The preparation method of modification infusorial earth-molecular sieve sorbing material
Wang et al. Column preconcentration of lead in aqueous solution with macroporous epoxy resin-based polymer monolithic matrix
CN116532094B (en) Ammonium phosphomolybdate resin particles, and preparation method and application thereof
CN104549183A (en) Silica gel chromatography packing and preparation method thereof
CN104689806B (en) Functionalized mesoporous SiO2/TiO2 composite nano-microsphere solid-phase extraction column and preparation method thereof
CN102452662B (en) Molecular sieve alkali metal ion exchange method
CN108801956A (en) Absorbing process of the chitosan to asparagine in sugarcane juice
CN104353441B (en) A kind of ion blotting material for enrichment water body ultra trace methyl mercury
JP6574299B2 (en) Improved aluminum doped chelating resin containing iminoacetic acid groups
CN107870136A (en) A kind of assay method of amphion sulfonated phenol formaldehyde resin cationic degree
CN105921116A (en) Cation exchange solid-phase extraction material with mixing effect mode and preparation method and application thereof
CN108854986A (en) A kind of epoxychloropropane modified chitosan and preparation method thereof for adsorbing heavy metal ion
CN102399342A (en) Surface functionalization method of poly (styrene-divinylbenzene) microspheres
WO2014041513A1 (en) A material used for phosphopeptide enrichment and a production method thereof
CN107570124A (en) Function monomer for preparing bisphenol-A trace mesoporous material and preparation method thereof
CN102731795A (en) Method for preparing ion exchange resin by adopting white carbon black as raw material
CN118258906A (en) A method for measuring the solid content of oil slurry by solid phase extraction separation
JP2006297244A (en) Pretreatment column for ion chromatography device, its regeneration method and ion chromatography device
CN214622475U (en) A pretreatment device for the determination of soluble salt components based on ion chromatography
AU2021106460A4 (en) Adsorbent film and its preparation and use
CN103940937B (en) Method for determining content of antibiotics in food or environmental sample by accelerated solvent extraction online purification method
CN102371147A (en) Preparation method of iodine removing agent
CN113030347A (en) Pretreatment device and method for determining soluble salt components based on ion chromatography

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
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20250815

Address after: 100078 Beijing City Chaoyang District Chaoyangmen North Street 22 No. 1202 room

Patentee after: Sinopec Petroleum Engineering Technology Service Co.,Ltd.

Country or region after: China

Patentee after: SINOPEC ZHONGYUAN PETROLEUM ENGINEERING Co.,Ltd.

Patentee after: DRILLING ENGINEERING TECHNOLOGY RESEARCH INSTITUTE OF SINOPEC ZHONGYUAN PETROLEUM ENGINEERING Co.,Ltd.

Address before: 100029 Beijing City, Chaoyang District Hui Street No. six twelfth floor

Patentee before: SINOPEC OILFIELD SERVICE Corp.

Country or region before: China

Patentee before: DRILLING ENGINEERING TECHNOLOGY RESEARCH INSTITUTE OF SINOPEC ZHONGYUAN PETROLEUM ENGINEERING Co.,Ltd.