Calculation Values of potential Stickiness (S*) and Apparent Activation Energy (AAE) from Adsorption of Some Aromatic Carboxylic Acids on the Surface of a New Adsorbent Substance

Khaleel Ibrahim Alniemi
{"title":"Calculation Values of potential Stickiness (S*) and Apparent Activation Energy (AAE) from Adsorption of Some Aromatic Carboxylic Acids on the Surface of a New Adsorbent Substance","authors":"Khaleel Ibrahim Alniemi","doi":"10.33899/EDUSJ.2020.126168.1021","DOIUrl":null,"url":null,"abstract":"This study includes calculation of the potential stickiness (S) and apparent activation energy (AAE) by the adsorption process of some aromatic carboxylic acids using sand (clay) as a new adsorbent material. This clay was collected from dust storms coming to the city of Mosul. The obtained results showed that physical adsorption which is achieved by applying the modified Arrhenius equation through the values of (S *) and (AAE) which have low values and bear a negative charge is preferable. Adsorption process occurs in two-step mechanism. The effect of the concentration of the acidic solution, temperature and the substituted groups SO3, NO2, OH, NH2 on the aromatic ring) was studied to clarify the nature of the association between organic carboxylic acid anions and inorganic metal oxides to form a complex surface model. The study concluded that the values of (S *) for all acids were less than one and they were more than the value of zero. Also, the values of (AAE) gave an indication that the adsorption process is exothermic and spontaneous. The presence of water molecules and (H) ions in solution is very important to change the nature of the clay surface. Keyword: Potential stickiness, apparent activation energy, aromatic carboxylic acids, new adsorbent material. Introduction: Adsorption is an effective and important method to remove pollution. It is simple and low-cost [1][2]. The substituted benzoic acids (5SSA, ONBA, OABA) are used in chemical industry, these acids are considered harmful substances for humans [3] [4] [5]. As an adsorbent material, Clay, consists of poly metal oxides from a rocky source [6] and different inorganic materials [7]. Metal oxides on the clay surface contain negative polar charges [8] as active sites that attract positive ions by absorbing them through physical forces. This type of attraction is called physical adsorption, while the chemical absorption occurs when the surface contains unsaturated electrons. Knowledge of adsorption mechanism is important for designing physical type of adsorption systems, through which absorbent material can be recovered and the process accomplished in an easy and Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 78 inexpensive way. The (AAE) values represent the desired degree of the optimum temperature to achieve the complete adsorption process. Whether it occurs spontaneously or not and whether the adsorption process is endothermic or exothermic, the positive or negative values of (AAE) give a good description of the thermodynamic condition for the adsorption process. Materials and Methods : 1The chemicals were used without further purification and they were supplied by Fluka and BDH companies. 2The new clay was used as an adsorbent material. This clay was collected (using clean and dry plastic containers) from dust storms that hit the city of Mosul. The clay has been sifted (filtered out) using a sieve (75) micrometer and the surface area was (3434) cm/gm. It was measured using the \"plaine device\" at the Technological Institute in Mosul. The clay components (listed in Table 1) were measured using X-rays Appearance-Type (pan analytical 7602 EA, Almelo) at Badush Cement Factory. Table 1. The components of clay 8.5 pH 37.36% CaO 19.71% SiO2 5.91% AL2O3 3.47% MgO 1.89% Fe2O3 0.48% SO3 3Preparation of solutions: aSolutions of three acids (5SSA, ONBA, OABA) at different concentrations using a mixture solvent (5% absolute ethanol and 95% distilled water) have been prepared. bStandard solution of (0.1), (0.01) M sodium hydroxide by titration with (potassium hydrogen phthalate) using (phenolphthalein) as indicator has been prepared. 4Study the adsorption process using batch method. 5A programmed water bath equipped with a vibrator at speed of 100 cycle/ min was used. 6An equal amount of adsorbent in the adsorption process for all concentrations was used. 7-The optimum conditions for adsorption were as follows: A-The weight of clay used =0.06 gm. B-Concentration of acids =5x10 molar C-The favorite pH = natural pH for each acid D-Contact time for each acid with percentage of adsorption is shown in table 2. Table (2). Contact time and percentage of adsorption for acids on clay surface at 25 C° Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 79 % Adsorption Contact time (min) Acid 76 40 5SSA 92 30 ONBA 74 40 OABA EThe adsorption process was studied at temperature ranging from (20-60) C° to obtain values of (S). FThe concentration of acid remaining in solution after the adsorption was calculated using spectrophotometric method. GThe amount of ions covered on the surface of the sorbent material was calculated at each concentration using different temperatures (20-60) ° C. HThe modified Arrhenius equation [9] that was applied, can be written as follows: S* = (1 θ) e Ea RT (modified Arrhenius equation) Ln (1 – θ) = ln S* Ea RT When draw Ln (1-θ) at (x) axis and 1 T at (y) axis gives intercept (Ln S*) while slope equal −Ea R which gives (AAE). 8The instruments: aVibratory water path type (julabo sw23). bElectric oven type (memmert). cDouble-beam spectrophotometer (schimaduz) model UV-1800. dThe surface area of the clay was measured using ( a plain) device and the amount of surface area was ( 3434 ) cm / gm . Results and Discussion: The modified Arrhenius equation (MAE) [9] depends on the amount of ions covering the surface at any concentration by using different temperatures. When experimental adsorption results are applied to (MAE), we obtain a value of (S *) through which the type of chemical or physical adsorption prevails. In addition, the value of (AAE) provides a qualitative description of the thermodynamic state of the adsorption process. The value of (S *), which represents the potential stickiness to the surface, is the preferred (adsorbed / adsorbent) system function of the range (o <s * <1) for the absorption process. This value depends on temperature and concentration. The values of (S *) can be calculated from the modified Arrhenius equation via the experimental results used. If S* >1, it means that the adsorbent substance is non-sticking on the adsorbed substance. If S* =1, it means that the liner relationship of stickiness between the adsorbed and adsorbent is predominated for a mixture of physical and chemical adsorption. S*=0 stickiness has occurred on adsorbed material and chemical absorption is predominant. If 0 < S , this represents the preferred stickiness of the adsorbent material on the clay, and the physical absorption is predominant. Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 80 In this study, the positive and negative values of (AAE) do not represent the areal activation energy, but rather give a description of the thermodynamic state of the adsorption process, since the acid ions prefer adsorption at low temperatures and the adsorption process is exothermic by nature .The low negative values of (AAE) give the conclusion that the adsorption process is a controlled diffusion process. The best value for (S) is shown when it is less than one. This indicates that the physical adsorption of ions occurs on the surface. In this case the adsorbent substance can be retrieved and used again, and this is economically important. Tables (3 – 5) Values of (S*) and (AAE) for (5SSA),( ONBA), (OABA) at different concentrations on the clay surface Table3 (5SSA) R AAE KJ/mole S* Conc(M) 0.9698 -21.100 142×10 0.005 0.9739 -2.646 0.1474 0.007 0.9529 -1.472 0.1560 0.009 0.9824 -1.168 0.3109 0.011 0.9979 -1.085 0.9078 0.013 Table 4(ONBA) Table 5(OABA) The results in tables (3-5) which refer to acids (5SSA,ONBA,BABA) at different concentrations. The used temperatures were ranged from (20-60)C at each concentration. Depending on the obtained results, the following conclusions can be reached: 1. The predominance of the physical adsorption in the adsorption process and this is preferred for the ease of recovery of the absorbent material [9][10]. 2. The increase in the concentration of the acid solution increases the values of (S*). This means that the conversion of the physical adsorption into a mixture of physical and chemical adsorption is at the highest concentration when the value of (S*) is one. Diluting the acidic concentration makes the value of (S*) very low because the ions have free movement within the solution (they easy move to the surface of the absorbent R2 AAE(Kj/mole) S* Conc(M) 0.97 -29.488 611×10 0.005 0.93 -4.568 0.0480 0.007 0.98 -2.547 0.1590 0.009 0.99 -1.397 0.3078 0.011 0.99 -0.961 0.4043 0.013 R AAE(Kj/mole) S* Conc(M) 0.99 -7.423 0.0125 0.005 0.99 -2.749 0.1460 0.007 0.99 -1.654 0.2878 0.009 0.99 -1.192 0.3905 0.011 0.99 -0.835 0.4885 0.013 Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 81 material (clay) as well as, the availability of the active sites on it which means that there is no competition between ions to adsorption on the surface. Thus the chemical adsorption becomes predominant. 3(AAE) values are negative and low, and they decrease as the concentration of the acid solution is increased by converting it from the highest negative values to the negative values that are close to the zero values. These results indicate that the adsorption process in the case of the acidic dilute solution (0.005) M prefers low temperature and ultimately it will be exothermic. This is because the ionic, molecular reaction and interferences are decreased in the case of the dilute acidic solution, then the adsorption process occurs spontaneously. Whereas in a concentrated acid solution (0.013) M , these interferences are increased, which leads to a decrease in the negative values of (AAE). This indicates the need for the adsorption system to have a low energy to complete the adsorption process, so that it turns from high spontaneously to low one. In addition, it converts from an exothermic to an endothermic process [9]","PeriodicalId":15610,"journal":{"name":"Journal of Education Science","volume":"74 1","pages":"76-89"},"PeriodicalIF":0.0000,"publicationDate":"2020-06-13","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Journal of Education Science","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.33899/EDUSJ.2020.126168.1021","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 1

Abstract

This study includes calculation of the potential stickiness (S) and apparent activation energy (AAE) by the adsorption process of some aromatic carboxylic acids using sand (clay) as a new adsorbent material. This clay was collected from dust storms coming to the city of Mosul. The obtained results showed that physical adsorption which is achieved by applying the modified Arrhenius equation through the values of (S *) and (AAE) which have low values and bear a negative charge is preferable. Adsorption process occurs in two-step mechanism. The effect of the concentration of the acidic solution, temperature and the substituted groups SO3, NO2, OH, NH2 on the aromatic ring) was studied to clarify the nature of the association between organic carboxylic acid anions and inorganic metal oxides to form a complex surface model. The study concluded that the values of (S *) for all acids were less than one and they were more than the value of zero. Also, the values of (AAE) gave an indication that the adsorption process is exothermic and spontaneous. The presence of water molecules and (H) ions in solution is very important to change the nature of the clay surface. Keyword: Potential stickiness, apparent activation energy, aromatic carboxylic acids, new adsorbent material. Introduction: Adsorption is an effective and important method to remove pollution. It is simple and low-cost [1][2]. The substituted benzoic acids (5SSA, ONBA, OABA) are used in chemical industry, these acids are considered harmful substances for humans [3] [4] [5]. As an adsorbent material, Clay, consists of poly metal oxides from a rocky source [6] and different inorganic materials [7]. Metal oxides on the clay surface contain negative polar charges [8] as active sites that attract positive ions by absorbing them through physical forces. This type of attraction is called physical adsorption, while the chemical absorption occurs when the surface contains unsaturated electrons. Knowledge of adsorption mechanism is important for designing physical type of adsorption systems, through which absorbent material can be recovered and the process accomplished in an easy and Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 78 inexpensive way. The (AAE) values represent the desired degree of the optimum temperature to achieve the complete adsorption process. Whether it occurs spontaneously or not and whether the adsorption process is endothermic or exothermic, the positive or negative values of (AAE) give a good description of the thermodynamic condition for the adsorption process. Materials and Methods : 1The chemicals were used without further purification and they were supplied by Fluka and BDH companies. 2The new clay was used as an adsorbent material. This clay was collected (using clean and dry plastic containers) from dust storms that hit the city of Mosul. The clay has been sifted (filtered out) using a sieve (75) micrometer and the surface area was (3434) cm/gm. It was measured using the "plaine device" at the Technological Institute in Mosul. The clay components (listed in Table 1) were measured using X-rays Appearance-Type (pan analytical 7602 EA, Almelo) at Badush Cement Factory. Table 1. The components of clay 8.5 pH 37.36% CaO 19.71% SiO2 5.91% AL2O3 3.47% MgO 1.89% Fe2O3 0.48% SO3 3Preparation of solutions: aSolutions of three acids (5SSA, ONBA, OABA) at different concentrations using a mixture solvent (5% absolute ethanol and 95% distilled water) have been prepared. bStandard solution of (0.1), (0.01) M sodium hydroxide by titration with (potassium hydrogen phthalate) using (phenolphthalein) as indicator has been prepared. 4Study the adsorption process using batch method. 5A programmed water bath equipped with a vibrator at speed of 100 cycle/ min was used. 6An equal amount of adsorbent in the adsorption process for all concentrations was used. 7-The optimum conditions for adsorption were as follows: A-The weight of clay used =0.06 gm. B-Concentration of acids =5x10 molar C-The favorite pH = natural pH for each acid D-Contact time for each acid with percentage of adsorption is shown in table 2. Table (2). Contact time and percentage of adsorption for acids on clay surface at 25 C° Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 79 % Adsorption Contact time (min) Acid 76 40 5SSA 92 30 ONBA 74 40 OABA EThe adsorption process was studied at temperature ranging from (20-60) C° to obtain values of (S). FThe concentration of acid remaining in solution after the adsorption was calculated using spectrophotometric method. GThe amount of ions covered on the surface of the sorbent material was calculated at each concentration using different temperatures (20-60) ° C. HThe modified Arrhenius equation [9] that was applied, can be written as follows: S* = (1 θ) e Ea RT (modified Arrhenius equation) Ln (1 – θ) = ln S* Ea RT When draw Ln (1-θ) at (x) axis and 1 T at (y) axis gives intercept (Ln S*) while slope equal −Ea R which gives (AAE). 8The instruments: aVibratory water path type (julabo sw23). bElectric oven type (memmert). cDouble-beam spectrophotometer (schimaduz) model UV-1800. dThe surface area of the clay was measured using ( a plain) device and the amount of surface area was ( 3434 ) cm / gm . Results and Discussion: The modified Arrhenius equation (MAE) [9] depends on the amount of ions covering the surface at any concentration by using different temperatures. When experimental adsorption results are applied to (MAE), we obtain a value of (S *) through which the type of chemical or physical adsorption prevails. In addition, the value of (AAE) provides a qualitative description of the thermodynamic state of the adsorption process. The value of (S *), which represents the potential stickiness to the surface, is the preferred (adsorbed / adsorbent) system function of the range (o 1, it means that the adsorbent substance is non-sticking on the adsorbed substance. If S* =1, it means that the liner relationship of stickiness between the adsorbed and adsorbent is predominated for a mixture of physical and chemical adsorption. S*=0 stickiness has occurred on adsorbed material and chemical absorption is predominant. If 0 < S , this represents the preferred stickiness of the adsorbent material on the clay, and the physical absorption is predominant. Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 80 In this study, the positive and negative values of (AAE) do not represent the areal activation energy, but rather give a description of the thermodynamic state of the adsorption process, since the acid ions prefer adsorption at low temperatures and the adsorption process is exothermic by nature .The low negative values of (AAE) give the conclusion that the adsorption process is a controlled diffusion process. The best value for (S) is shown when it is less than one. This indicates that the physical adsorption of ions occurs on the surface. In this case the adsorbent substance can be retrieved and used again, and this is economically important. Tables (3 – 5) Values of (S*) and (AAE) for (5SSA),( ONBA), (OABA) at different concentrations on the clay surface Table3 (5SSA) R AAE KJ/mole S* Conc(M) 0.9698 -21.100 142×10 0.005 0.9739 -2.646 0.1474 0.007 0.9529 -1.472 0.1560 0.009 0.9824 -1.168 0.3109 0.011 0.9979 -1.085 0.9078 0.013 Table 4(ONBA) Table 5(OABA) The results in tables (3-5) which refer to acids (5SSA,ONBA,BABA) at different concentrations. The used temperatures were ranged from (20-60)C at each concentration. Depending on the obtained results, the following conclusions can be reached: 1. The predominance of the physical adsorption in the adsorption process and this is preferred for the ease of recovery of the absorbent material [9][10]. 2. The increase in the concentration of the acid solution increases the values of (S*). This means that the conversion of the physical adsorption into a mixture of physical and chemical adsorption is at the highest concentration when the value of (S*) is one. Diluting the acidic concentration makes the value of (S*) very low because the ions have free movement within the solution (they easy move to the surface of the absorbent R2 AAE(Kj/mole) S* Conc(M) 0.97 -29.488 611×10 0.005 0.93 -4.568 0.0480 0.007 0.98 -2.547 0.1590 0.009 0.99 -1.397 0.3078 0.011 0.99 -0.961 0.4043 0.013 R AAE(Kj/mole) S* Conc(M) 0.99 -7.423 0.0125 0.005 0.99 -2.749 0.1460 0.007 0.99 -1.654 0.2878 0.009 0.99 -1.192 0.3905 0.011 0.99 -0.835 0.4885 0.013 Ind Calculation Values of potential Stickiness (S*) and Apparent Activation..... 81 material (clay) as well as, the availability of the active sites on it which means that there is no competition between ions to adsorption on the surface. Thus the chemical adsorption becomes predominant. 3(AAE) values are negative and low, and they decrease as the concentration of the acid solution is increased by converting it from the highest negative values to the negative values that are close to the zero values. These results indicate that the adsorption process in the case of the acidic dilute solution (0.005) M prefers low temperature and ultimately it will be exothermic. This is because the ionic, molecular reaction and interferences are decreased in the case of the dilute acidic solution, then the adsorption process occurs spontaneously. Whereas in a concentrated acid solution (0.013) M , these interferences are increased, which leads to a decrease in the negative values of (AAE). This indicates the need for the adsorption system to have a low energy to complete the adsorption process, so that it turns from high spontaneously to low one. In addition, it converts from an exothermic to an endothermic process [9]
一种新型吸附剂表面吸附芳香族羧酸的潜在粘性(S*)和表观活化能(AAE)的计算值
计算了砂(粘土)作为新型吸附剂吸附芳香族羧酸过程的潜在黏度(S)和表观活化能(AAE)。这些粘土是从摩苏尔市的沙尘暴中收集来的。结果表明,采用修正的Arrhenius方程,通过低值带负电荷的(S *)和(AAE)进行物理吸附效果较好。吸附过程采用两步法。研究了酸性溶液浓度、温度和取代基(SO3、NO2、OH、NH2)对芳环的影响,阐明了有机羧酸阴离子与无机金属氧化物缔合形成复杂表面模型的性质。研究得出结论,所有酸的(S *)值都小于1,大于0。(AAE)值表明吸附过程是自发的、放热的。水分子和(H)离子在溶液中的存在对改变粘土表面的性质是非常重要的。关键词:潜在粘性,表观活化能,芳香羧酸,新型吸附材料。导读:吸附是一种有效而重要的去除污染的方法。这是简单和低成本[1]b[2]。取代苯甲酸(5SSA, ONBA, OABA)用于化学工业,这些酸被认为是对人体有害的物质[3]b[4][5]。粘土是一种吸附剂,由来自岩石源[6]的多金属氧化物和不同的无机材料[7]组成。粘土表面的金属氧化物含有负极电荷[8],作为通过物理力吸收正离子的活性位点。这种类型的吸引称为物理吸附,而化学吸收发生在表面含有不饱和电子时。了解吸附机理对于设计物理类型的吸附系统是很重要的,通过这种系统可以回收吸收材料,并在一个简单的过程中完成吸附过程便宜的方法。(AAE)值代表实现完全吸附过程所需的最佳温度的程度。无论是否自发发生,无论吸附过程是吸热还是放热,(AAE)的正值或负值都能很好地描述吸附过程的热力学条件。材料和方法:1 .化学物质未经进一步纯化,由Fluka和BDH公司提供。该新型粘土被用作吸附剂材料。这些粘土是从袭击摩苏尔市的沙尘暴中收集来的(使用干净干燥的塑料容器)。粘土用(75)微米筛过(滤出),表面积为(3434)cm/gm。它是在摩苏尔技术研究所使用“平面装置”测量的。在Badush水泥厂使用x射线外观型(pan - analytical 7602 EA, Almelo)测量粘土成分(见表1)。表1。粘土组成8.5 pH 37.36% CaO 19.71% SiO2 5.91% AL2O3 3.47% MgO 1.89% Fe2O3 0.48% SO3溶液制备:以5%无水乙醇和95%蒸馏水为混合溶剂,制备了3种不同浓度的酸(5SSA, ONBA, OABA)溶液。以(酚酞)为指示剂,用(邻苯二甲酸氢钾)滴定制得(0.1),(0.01)M氢氧化钠的标准溶液。采用间歇法研究吸附过程。采用5A程控水浴,配有振动器,速度为100循环/分钟。6在所有浓度的吸附过程中使用等量的吸附剂。7 .最佳吸附条件为:a .粘土用量=0.06 gm。b .酸浓度=5 × 10 mol / l。c .最佳pH =每种酸的自然pH。d .每种酸与吸附率的接触时间见表2。表(2)25℃时粘土表面酸的接触时间和吸附百分比。潜在粘性(S*)和表观活化计算值.....79 %吸附接触时间(min)酸76 40 5SSA 92 30 ONBA 74 40 OABA在(20-60)℃的温度范围内对吸附过程进行研究,得到吸附后溶液中残留酸的浓度(S)。g在不同温度(20-60)℃下,计算不同浓度下吸附材料表面覆盖的离子量。 此外,它从放热过程转变为吸热过程
本文章由计算机程序翻译,如有差异,请以英文原文为准。
求助全文
约1分钟内获得全文 求助全文
来源期刊
自引率
0.00%
发文量
0
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
确定
请完成安全验证×
copy
已复制链接
快去分享给好友吧!
我知道了
右上角分享
点击右上角分享
联系我们:info@booksci.cn Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。 Copyright © 2023 布克学术 All rights reserved.
京ICP备2023020795号-1
ghs 京公网安备 11010802042870号
Book学术文献互助
Book学术文献互助群
群 号:481959085
Book学术官方微信