<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AJAC</journal-id><journal-title-group><journal-title>American Journal of Analytical Chemistry</journal-title></journal-title-group><issn pub-type="epub">2156-8251</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ajac.2022.1310026</article-id><article-id pub-id-type="publisher-id">AJAC-120878</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Chemistry&amp;Materials Science</subject></subj-group></article-categories><title-group><article-title>
 
 
  Spectrophotometric Method for Determination of Chromium Ion in Aqueous Solution Using Ninhydrin
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Hutaf</surname><given-names>Mustafa Baker</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Tiba</surname><given-names>Dheyaa Rahoomi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Hamzeh</surname><given-names>Abdel-Halim</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Department of Chemistry, Hashemite University, Zarqa, Jordan</addr-line></aff><aff id="aff1"><addr-line>Department of Chemistry, Faculty of Science, Al Al-Bayt University, Mafraq, Jordan</addr-line></aff><pub-date pub-type="epub"><day>28</day><month>10</month><year>2022</year></pub-date><volume>13</volume><issue>10</issue><fpage>382</fpage><lpage>398</lpage><history><date date-type="received"><day>3,</day>	<month>August</month>	<year>2022</year></date><date date-type="rev-recd"><day>28,</day>	<month>October</month>	<year>2022</year>	</date><date date-type="accepted"><day>31,</day>	<month>October</month>	<year>2022</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  A simple, precise, inexpensive and reproducible spectrophotometric method was investigated for the determination of chromium ion (III) in aqueous media, this method based on the formation of a complex between chromium ion (III) and ninhydrin, a deep greenish-violet colored product in the presence of potassium hydroxide was obtained. The absorption of this product was measured at 
  λ
  <sub>max</sub> = 375 nm. The reaction proceeds quantitatively at room temperature. The linear calibration curve was constructed over range of (4.8 &#215; 10
  <sup>-4</sup> - 1.6 &#215; 10
  <sup>-2</sup>) mol/L of chromium ions with molar absorptivity of 2.90 &#215; 10
  <sup>2</sup> and correlation coefficient R
  <sup>2</sup> = 0.9989. The calculated Sandell’s sensitivity value is 0.179 μg/cm
  <sup>2</sup>, the limits of detection (LOD) and the limit of quantification (LOQ) are found to be 3.74 &#215; 10
  <sup>-5</sup> and 1.24 &#215; 10
  <sup>-4</sup> mol/L, respectively. The method was successfully applied for determination of the chromium ion in aqueous solution. The stoichiometry of the reactions was determined molar combining ratio of 1:2 between chromium and ninhydrin.
 
</p></abstract><kwd-group><kwd>Ninhydrin</kwd><kwd> Chromium Ions</kwd><kwd> Spectroscopy</kwd><kwd> Stoichiometry</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The identification of harmful chemicals in sewage, industrial, and mining waste effluents has been the subject of extensive research in recent years. Several different sorts of health issues in people, plants, and animals have been caused by their presence in streams and lakes. Chromium ions are one of these toxic inorganic substances.</p><p>One of the most prevalent elements in nature is chromium. Chromium levels in the environment have gradually risen as a result of industrial activity, particularly that of tanneries, mines, and incinerators. The most common forms of chromium in natural media are hydrated chromium (III) species and chromium (Vl) (chromate). Trivalent chromium is contained in biological tissues and aids in the maintenance of proper glucose, protein, and fat metabolism [<xref ref-type="bibr" rid="scirp.120878-ref1">1</xref>], whereas chrome (Vl) (chromate) has unquestionably harmful effects on living things, including humans, and potentially carcinogenic and mutagenic qualities. Recent publications of in-depth studies of the analytical techniques used to determine chromium in liquid and solid matrices reflect the ongoing interest in dangerous element monitoring [<xref ref-type="bibr" rid="scirp.120878-ref2">2</xref>].</p><p>The aquatic animal and plant life are affected by chromium traces in seawater. Waste waters from industries including paint, pigment, dye, mordant, rubber, plastic, ceramic, textile, leather, tannery, welding process, smelting works, chrome plating facilities, steel and its alloys are the main sources of metal discharge into the environment that results in chromium pollution. Another significant source of chromium pollution comes from cooling fluids used in industry. According to the drinking water standards provided by the Indian Standards and the United States Public Health Department, the maximum permitted content of chromium is mostly 50 &#181;g&#183;L<sup>−1</sup> [<xref ref-type="bibr" rid="scirp.120878-ref3">3</xref>].</p><p>There are several methods for chromium ion measurement in the literature; the most frequently used are ultraviolet-visible (UV-Vis) spectrophotometry [<xref ref-type="bibr" rid="scirp.120878-ref4">4</xref>], high-performance liquid chromatography [<xref ref-type="bibr" rid="scirp.120878-ref5">5</xref>], capillary electrophoresis [<xref ref-type="bibr" rid="scirp.120878-ref6">6</xref>], Adsorptive Stripping Voltammetry [<xref ref-type="bibr" rid="scirp.120878-ref7">7</xref>], flame and furnace atomic adsorption spectroscopy [<xref ref-type="bibr" rid="scirp.120878-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref9">9</xref>], and mass spectrometry [<xref ref-type="bibr" rid="scirp.120878-ref10">10</xref>]. Because of its simplicity, sensitivity, accuracy, and speed, the spectrophotometric method holds a special place in science. This technique became essential to contemporary analytical chemists due to the instrument’s accessibility. The absorption of light is the foundation for spectrophotometric procedures used to identify substances [<xref ref-type="bibr" rid="scirp.120878-ref11">11</xref>].</p><p>In this research, a new spectrophotometric method for the determination of Cr (III) using ninhydrin was investigated, Ninhydrin in this research acts as chromogenic agent [<xref ref-type="bibr" rid="scirp.120878-ref12">12</xref>]. The ability of ninhydrin (a bidentate ligand) to function as an analytical reagent was the subject of some interesting and practical data presented in this work [<xref ref-type="bibr" rid="scirp.120878-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref15">15</xref>]. The chromogenic reagent in this procedure was ninhydrin. The produced stable colored complex was measured at λ<sub>max</sub> = 375 nm under variable conditions. The calibration curve was constructed under optimum conditions. This method found to be rapid, sensitive, simple and reproducible one.</p></sec><sec id="s2"><title>2. Experimental</title><sec id="s2_1"><title>2.1. Apparatus and Instruments</title><p>The instrument that used in this research are UV\Vis spectrometer (SPECORD S600), Analytical balance (METTLER TOLEDO, AL 104) and Digital pH meter (METTLER TOLEDO, Seven Easy) shaker water bath (GFL 10983), Hot plate stirrer (HP-3000) and Heating Drying oven (Model DHG).</p></sec><sec id="s2_2"><title>2.2. Reagents and Chemicals</title><p>An analytical grade chemical reagents were used, as received without further treatment Cr(NO<sub>3</sub>) 39H<sub>2</sub>O 98% Panreac, Ninhydrin 98.0% GCC Company, KOH 98.0% NTL (NEN TECH LTD), NaCl 99.0% GCC Company, KNO<sub>3</sub> 99.0% S.D Fine.chem. LTD, CaCl<sub>2</sub> 98.0% s S.D Fine-CHEM LTD INE, CuSO<sub>4</sub> 98.0% LOBA chemie and ZnCl<sub>2</sub> 98.0% GCC Company.</p></sec><sec id="s2_3"><title>2.3. Selection of the Optimum Wavelength</title><p>Many experiments were done to find the optimum wavelength which is the maximum one for the product of the reaction between Cr<sup>3+</sup> ions with ninhydrin. All the experiments were done in alkaline media using 0.0089 M of KOH, at room temperature and with final volume of 50 mL. A stable greenish-violet colored complex (Cr<sup>3+</sup> - ninhydrin) was obtained after many trials after 15 minutes, and its maximum value of absorption was found at 375 nm in the visible region using 6.24 &#215; 10<sup>−3</sup> M of Cr<sup>3+</sup> ions with 2.4 &#215; 10<sup>−3</sup> M of ninhydrin. At each trial the absorbance was measured in the range of wave length (350 - 700) nm. The spectra of the each blank and 6.24 &#215; 10<sup>−3</sup> M of Cr<sup>3+</sup> ions solutions were measured separately also in the range of wave length (350 - 700) nm as shown in Figures 1-3.</p></sec><sec id="s2_4"><title>2.4. Variables Studies</title><p>Different parameters were used to get the best circumstances for the reaction between chromium ions and ninhydrin. The following variables were examined to develop this analytical method: contact time, temperature, initial ninhydrin concentration, initial chromium ion concentration, initial concentration of KOH. The thermodynamic and kinetic studies were done at the found optimum conditions.</p></sec><sec id="s2_5"><title>2.5. Effect of Reaction Time</title><p>Three prepared solutions which of Cr<sup>3+</sup>, ninhydrin and KOH which have the following concentration respectively 6.24 &#215; 10<sup>−3</sup> M, 2.4 &#215; 10<sup>−3</sup> M and of 8.9 &#215; 10<sup>−3</sup> M are mixed with together at room temperature with final volume of 50 mL to investigate the effect of time of reaction on the absorbance of the colored product. The intervals time were 5, 10, 15, &#183;&#183;&#183; until 155 minutes. The absorbance of the product was measured every 5.0 minutes over the 155 minutes. All of the experiments were repeated and the average result was taken.</p></sec><sec id="s2_6"><title>2.6. Initial Chromium Ions Concentration</title><p>Different initial concentrations of Cr<sup>3+</sup> ions were prepared in the range of (2.00 &#215; 10<sup>−4</sup> - 1.86 &#215; 10<sup>−2</sup>) M, each single solution was mixed separately with constant amount of each KOH with final concentrations of 0.0089 M and ninhydrin with final concentration of 0.0024 M. The solution was left for 15 min to complete the reaction and developing the deep greenish-violet colored complex with constant intensity the solution was diluted to 50 mL using distilled water. The absorbance was measured at 375 nm. All of the experiments were repeated and the average result was taken.</p></sec><sec id="s2_7"><title>2.7. Effect of Initial Concentration of Ninhydrin</title><p>By measuring the absorbance of solutions containing fixed concentrations of both Cr<sup>3+</sup> (6.24 &#215; 10<sup>−3</sup> M) and KOH (8.9 &#215; 10<sup>−3</sup> M) together with varying concentrations of ninhydrin (4.8 &#215; 10<sup>−4</sup> - 9.6 &#215; 10<sup>−3</sup> M) in a final volume of 50 mL, it was possible to determine the impact of ninhydrin concentration on the intensity of the colored complex at the chosen wavelength which is at 375 nm, the absorbance of each solution was determined. The average outcome was determined after repeating each experiment.</p></sec><sec id="s2_8"><title>2.8. Effect of Initial Concentration of KOH</title><p>The effects of the initial potassium hydroxide concentration on the outcomes of this combination were investigated through a number of experiments while keeping the other conditions constant, the concentrations of both Cr<sup>3+</sup> of 6.24 &#215; 10<sup>−3</sup> M and ninhydrin of 2.4 &#215; 10<sup>−3</sup> M also kept constant, different volumes of 0.0089 M of KOH were transfers into a series of 50 ml volumetric flask 0, 1, 3, 5, 7, 9, 11, 13, 15, 17, 19 mL these solutions were completed to final volume. At 375 nm, the absorbance of each solution was determined. The average outcome was determined after repeating each experiment.</p></sec><sec id="s2_9"><title>2.9. Effect of Solution Temperature</title><p>The following temperatures were chosen: R.T (room temperature), 15˚C, 20˚C, 25˚C, 30˚C, 35˚C, 40˚C, 45˚C, 50˚C, 55˚C, and 60˚C. Several tests were conducted to examine the impact of temperature on the stability of the complex (Cr-Ninhydrin). The concentration of Cr<sup>3+</sup> is 6.24 &#215; 10<sup>−3</sup> M, ninhydrin is 2.4 &#215; 10<sup>−3</sup> M, and KOH is 8.9&#215; 10<sup>−3</sup> M, with other conditions being held constant. At 375 nm, the absorbance of each solution was determined. After conducting each experiment a second time, the average result was established.</p></sec><sec id="s2_10"><title>2.10. Effect of Interfering Ions</title><p>The experiment was conducted using 50 mL volumetric flasks containing 3.12 &#215; 10<sup>−3</sup> M of Cr<sup>3+</sup>, 8.9 &#215; 10<sup>−3</sup> M of KOH, and 2.4 &#215; 10<sup>−3</sup> M of ninhydrin under the optimum conditions. Separate amounts of the ionic salts NaCl, NaNO<sub>3</sub>, ZnSO<sub>4</sub> and CaCl<sub>2</sub> were added separately to each flask before filling it to the mark. The absorbance of each individual solution was then measured at 375 nm. The average outcome was determined after repeating each experiment.</p></sec><sec id="s2_11"><title>2.11. Construction of the Calibration Curve</title><p>The calibration curve was created using the spectrophotometric method under the ideal conditions: the concentration of Ninhydrin is 2.4 &#215; 10<sup>−3</sup> M and 8.9 &#215; 10<sup>−3</sup> M KOH kept constant while different initial concentration of Cr<sup>3+</sup> ions were used. The final volume of each solution is 50 mL using volumetric flask, After 15 minutes, and the reaction of each solution results in a greenish-violet color. The solution is then diluted to the appropriate concentration with The absorbance in the visible range was measured in comparison to a reagent blank made in the same way but without Cr<sup>3+</sup> and kept at room temperature.</p></sec><sec id="s2_12"><title>2.12. Validation Parameters</title>Accuracy and Precision<p>The method’s precision was calculated using intermediate precision (intra-day and inter-day). On the same day (with intra-day precision) and four days in a row, three replicates of three distinct standard Cr<sup>3+</sup> concentrations were examined (inter-day precision). The similarity of the reference value and the obtained value is what determines how accurate an analytical procedure is.</p></sec><sec id="s2_13"><title>2.13. Studying the Kinetic</title><sec id="s2_13_1"><title>2.13.1. Initial Rate Method</title><p>Under the ideal conditions; five experiments with various concentration of Cr<sup>3+</sup> were prepared in the range of (0.0011 - 0.016) M in 50 mL volumetric flasks. After 15 minutes, successive additions of distilled water brought the volume up to the desired level. After thoroughly mixing the contents of each flask, the absorbance was measured at 375 nm as a function of time. The slope of the tangent to the absorbance-time plot was used to calculate the initial rate constant of the reaction (k) at various concentrations. Plotting the initial reaction rate constant (k) against the molar concentration of the Cr<sup>3+</sup> ions resulted in the calibration graphs.</p></sec><sec id="s2_13_2"><title>2.13.2. Fixed Time Method</title><p>The absorbance of each sample of Cr<sup>3+</sup> solution was measured at 375 nm in accordance with a reagent blank made similarly but without the Cr<sup>3+</sup> solution, also at the most favorable experimental conditions previously mentioned. At regular intervals of 2 minutes, the absorbance of each solution was measured as a function of time. Between the times t1 (2 min) and t2 (4, 6, 8, 20 min), the change in absorbance (ΔA) was estimated. Plotting the absorbance against the initial concentration of Cr<sup>3+</sup> ions and this process was repeated for each concentration of Cr<sup>3+</sup> ions produced the calibration curve.</p></sec></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Effect of Contact Time</title><p>The optimum contact time of the reaction between the chromium ions and ninhydrin was reached by following the development of the maximum absorbance at specific time at room temperature, several experiments were done to investigate the influence of time on the absorbance of the Cr<sup>3+</sup>–ninhydrin reaction, whilst the other conditions remained constant, The following time intervals were recorded: 5, 10, 15, 30, &#183;&#183;&#183;, and 155 minutes. Every 5 minutes, the product’s absorbance was measured over the 155 minutes, after 5 minutes of reaction the initial absorbance was 0.67 then it is increasing until reaching 0.73 after 15 minutes, which is the time for the full developed color of the product, at 20 minutes and after the signal of absorbance decreasing to reach 0.1 at 155 minutes as shown in <xref ref-type="fig" rid="fig4">Figure 4</xref>. Dissociation of this complex may begin to occur after about 20 minutes. The optimum time for measurement of this complex is after about 15 minutes.</p></sec><sec id="s3_2"><title>3.2. Effect of Initial Concentration of Cr<sup>3+</sup> Ion</title><p>The effect of initial concentration Cr<sup>3+</sup> was investigated while keeping the other variables constant. As was observed from <xref ref-type="fig" rid="fig5">Figure 5</xref>, the absorbance of the</p><p>complex increased by increasing the concentration of Cr<sup>3+</sup> ions in the range (0.0008 - 0.02) M while the concentration of ninhydrin kept constant, then sharp decreasing in the absorbance was observed by raising the concentration of Cr<sup>3+</sup> ions in the range of (0.024 - 0.04) M, this decreasing may be due to the dissociation of the complex as the concentration of metal ions increased, the equilibrium of reaction will shift to left.</p></sec><sec id="s3_3"><title>3.3. Effect of Ninhydrin Initial Concentration</title><p>Various ninhydrin concentrations between (4.8 &#215; 10<sup>−4</sup> - 2.1 &#215; 10<sup>−2</sup>) M were added to constant concentration of Cr<sup>3+</sup> ions, the other variables kept constant, According to the standard procedure, the absorbance was measured. <xref ref-type="fig" rid="fig6">Figure 6</xref> shows how the concentration of ninhydrin affects the intensity of the produced complex. The findings show that the absorbance decreases as ninhydrin solution concentrations increase.</p><p>The findings show that the absorbance of the complex decreases as ninhydrin solution concentrations increase because the intensity of the colored complex increased, the absorbance reached the maximum value when 2.4 &#215; 10<sup>−3</sup> M of ninhydrin is used, the decreasing in absorbance was noticed when higher concentration of ninhydrin is used, dissociation of the complex may occurred by increasing ninhydrin concentration.</p><p>According to the accepted practice, the absorbance was measured. Figureshows how the concentration of ninhydrin affects the complex (6). The findings show that the absorbance decreases as ninhydrin solution concentrations increase.</p></sec><sec id="s3_4"><title>3.4. Effect of Temperature</title><p>The influence of temperature was investigated at various temperature intervals were chosen in the range of 15˚C until reaching 60˚C as shown in <xref ref-type="fig" rid="fig7">Figure 7</xref>, the temperature values from 15˚C to 40˚C showed that the stability of the formed</p><p>colored complex has not been impacted, while in the range of 45˚C to 60˚C the stability decreased gradually and the color of the complex became less dense, and decreasing in absorbance readings was observed. This mean that the reaction is stable at low and moderately high temperature range, while at higher temperature instability of the complex is observed which means an exothermic reaction may be occurs.</p></sec><sec id="s3_5"><title>3.5. Effect Concentration KOH</title><p>Investigations were also done into the effect of KOH concentration on the reaction product’s absorbance. From <xref ref-type="fig" rid="fig8">Figure 8</xref>, it was observed that the absorbance</p><p>of this colored complex decreased when the KOH concentration was raised until it was zero. A competition between ninhydrin and OH<sup>-</sup> to interact with the Cr<sup>3+</sup> ions may occurred and another complex was formed.</p></sec><sec id="s3_6"><title>3.6. Effect of Interfering Ions on Complex Stability</title><p>The impact of foreign species frequently discovered with Cr<sup>3+</sup> were examined under optimal conditions to evaluate the efficiency of the suggested technique by adding known concentrations of diverse ions of standard Cr<sup>3+</sup>, the influence of three different cations on the determination of Cr<sup>3+</sup> was investigated and results are shown in <xref ref-type="table" rid="table1">Table 1</xref>. The results indicate that almost all salts had no effect on absorbance reading and hence have no influence on complex stability.</p></sec><sec id="s3_7"><title>3.7. Linearity, Detection and Quantification Limits</title><p>Based on Beer’s Lambert law, the linear correlation coefficient between absorbance and Cr<sup>3+</sup> ion concentration was determined, from the regression analysis the data used to estimate the intercept (a), slope (b), and the correlation coefficient (R<sup>2</sup>) as can we see in <xref ref-type="table" rid="table2">Table 2</xref> and illustrated in <xref ref-type="fig" rid="fig9">Figure 9</xref>, the limit of detection and the limit of quantification also contained in <xref ref-type="table" rid="table2">Table 2</xref>.</p></sec><sec id="s3_8"><title>3.8. Precision</title><p>With three different Cr<sup>3+</sup> solution concentrations, the precision and accuracy were studied. The precision was confirmed [<xref ref-type="bibr" rid="scirp.120878-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref17">17</xref>] in terms of intra-day intermediate precision, and these solutions were created and merged with ninhydrin under the optimal conditions. For intra-day precision, the products were examined three times on the same day. For each concentration of Cr<sup>3+</sup> ions, the standard deviation (SD) and relative standard deviation (%RSD) were estimated, and the range of (%RSD) for the three different concentrations was 0.90% - 3.18% as shown in <xref ref-type="table" rid="table3">Table 3</xref>. The repeatability in three days (inter-day) for each</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Effect of foreign ions from different salts on the determination Cr<sup>3+</sup> = 6.24 &#215; 10<sup>−3</sup> M and 2.4 &#215; 10<sup>−3</sup> M of Ninhydrin at room temperature</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Cr<sup>3</sup><sup>+</sup> solution number</th><th align="center" valign="middle" >Absorbance (Without interfering salts)</th><th align="center" valign="middle" >Interfering salts</th><th align="center" valign="middle" >Absorbance (with interfering salts)</th><th align="center" valign="middle" >% Interference</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.81</td><td align="center" valign="middle" >NaCl</td><td align="center" valign="middle" >0.80</td><td align="center" valign="middle" >1.23</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.83</td><td align="center" valign="middle" >NaNO<sub>3</sub></td><td align="center" valign="middle" >0.81</td><td align="center" valign="middle" >2.4</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.82</td><td align="center" valign="middle" >CaCl<sub>2</sub></td><td align="center" valign="middle" >0.83</td><td align="center" valign="middle" >1.22</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.85</td><td align="center" valign="middle" >ZnSO<sub>4</sub></td><td align="center" valign="middle" >0.80</td><td align="center" valign="middle" >5.88</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Analytical parameters for the developed spectrophotometric method of the determination of Cr<sup>3+</sup> using ninhydrin</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Parameter</th><th align="center" valign="middle" >Value</th></tr></thead><tr><td align="center" valign="middle" >Color</td><td align="center" valign="middle" >Deep greenish-violet</td></tr><tr><td align="center" valign="middle" >max (nm)</td><td align="center" valign="middle" >375</td></tr><tr><td align="center" valign="middle" >Linearity range (mol/l)</td><td align="center" valign="middle" >(4.8 &#215; 10<sup>−4</sup> - 1.6 &#215; 10<sup>−2</sup>)</td></tr><tr><td align="center" valign="middle" >(L/mol/cm)</td><td align="center" valign="middle" >2.90 &#215; 10<sup>2</sup></td></tr><tr><td align="center" valign="middle" >Range time for Color stability</td><td align="center" valign="middle" >15</td></tr><tr><td align="center" valign="middle" >pH</td><td align="center" valign="middle" >10</td></tr><tr><td align="center" valign="middle" >Sandell’s sensitivity</td><td align="center" valign="middle" >0.179 &#181;g /cm<sup>2</sup></td></tr><tr><td align="center" valign="middle" >Temperature ˚C</td><td align="center" valign="middle" >Room temperature</td></tr><tr><td align="center" valign="middle" >Correlation coefficient (R<sup>2</sup>)</td><td align="center" valign="middle" >0.9989</td></tr><tr><td align="center" valign="middle" >LOD (&#181;g&#183;mL<sup>−1</sup>)</td><td align="center" valign="middle" >9.12 &#215; 10<sup>−6</sup></td></tr><tr><td align="center" valign="middle" >LOQ (&#181;g&#183;mL<sup>−1</sup>)</td><td align="center" valign="middle" >3.04 &#215; 10<sup>−5</sup></td></tr><tr><td align="center" valign="middle" >LOL</td><td align="center" valign="middle" >6.24 &#215; 10<sup>−3</sup></td></tr></tbody></table></table-wrap><p>The absorbance measured in a glass cuvette of-section are 1 cm<sup>2</sup>.</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Evaluation of intra-day and inter-day accuracy and precision</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Method</th><th align="center" valign="middle" >[Cr<sup>3+</sup>] taken mol/L</th><th align="center" valign="middle" >[Cr<sup>3+</sup>] found mol/L</th><th align="center" valign="middle" >Absolute error</th><th align="center" valign="middle" >% RSD</th></tr></thead><tr><td align="center" valign="middle"  rowspan="3"  >Intra-day Accuracy and precision</td><td align="center" valign="middle" >0.00110</td><td align="center" valign="middle" >0.00130</td><td align="center" valign="middle" >0.00020</td><td align="center" valign="middle" >0.90</td></tr><tr><td align="center" valign="middle" >0.00400</td><td align="center" valign="middle" >0.00380</td><td align="center" valign="middle" >−0.00020</td><td align="center" valign="middle" >5.40</td></tr><tr><td align="center" valign="middle" >0.00080</td><td align="center" valign="middle" >0.00084</td><td align="center" valign="middle" >0.00040</td><td align="center" valign="middle" >3.18</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Inter-day Accuracy and precision</td><td align="center" valign="middle" >0.00110</td><td align="center" valign="middle" >0.00132</td><td align="center" valign="middle" >0.00022</td><td align="center" valign="middle" >1.24</td></tr><tr><td align="center" valign="middle" >0.00400</td><td align="center" valign="middle" >0.00494</td><td align="center" valign="middle" >0.00094</td><td align="center" valign="middle" >1.78</td></tr><tr><td align="center" valign="middle" >0.00080</td><td align="center" valign="middle" >0.00087</td><td align="center" valign="middle" >0.00007</td><td align="center" valign="middle" >3.71</td></tr></tbody></table></table-wrap><p>concentration of Cr<sup>3+</sup> ions in terms of %RSD were acquired in the range 1.24% - 3.71%. The precision was also determined in terms of intermediate precision inter-day. The products were examined in three repeats over three consecutive</p><p>days (inter-day precision) by selecting three different concentrations of Cr<sup>3+</sup> ions that mixed with ninhydrin under the optimal parameters.</p></sec><sec id="s3_9"><title>3.9. Accuracy</title><p>Investigation of the analytical method’s accuracy resulted in the calculation of the absolute error for each analysis (both intra- and inter-day accuracy), as indicated in <xref ref-type="table" rid="table3">Table 3</xref>. The taken amount and the found amount are likely close to one another based on the minimal absolute error values [<xref ref-type="bibr" rid="scirp.120878-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref17">17</xref>]. The F-test was used in the statistical analysis for the intraday and interlay, and the results demonstrated that there is no bias between the taken values and the observed ones at alpha = 0.05, disproving the null hypothesis.</p></sec><sec id="s3_10"><title>3.10. Stoichiometry of the Reaction</title><p>By using the limiting logarithmic technique under ideal conditions, the stoichiometric ratio between the Cr<sup>3+</sup> ion and the ninhydrin was assessed [<xref ref-type="bibr" rid="scirp.120878-ref18">18</xref>]. Two sets of tests were made using this method: the first set varied the concentration of Cr<sup>3+</sup> while maintaining a constant concentration of ninhydrin, and the second set varied the concentration of Cr<sup>3+</sup> while maintaining a constant concentration of ninhydrin. To identify the order of reaction of the Cr<sup>3+</sup> with respect to ninhydrin or vice versa, log absorbance versus log [Cr<sup>3+</sup>] and log ninhydrin were plotted to evaluate the slope of the corresponding line, as shown in <xref ref-type="fig" rid="fig10">Figure 10</xref>. It was observed that the slope was 1.0049 for various concentrations of Cr<sup>3+</sup>. The slope of <xref ref-type="fig" rid="fig11">Figure 11</xref> is at varying ninhydrin concentrations. At different ninhydrin concentrations, the slope from <xref ref-type="fig" rid="fig11">Figure 11</xref> was equal to about 2. This validated the 1:2 molar ratio of coupling between Cr<sup>3+</sup> and ninhydrin.</p><p>Depending on the data that obtained from <xref ref-type="fig" rid="fig10">Figure 10</xref> and <xref ref-type="fig" rid="fig11">Figure 11</xref>, the proposed chemical equation of the reaction between Cr<sup>3+</sup> and ninhydrin is shown at Scheme 1.</p></sec><sec id="s3_11"><title>3.11. Kinetic Studies</title><sec id="s3_11_1"><title>3.11.1. Initial Rate of Reaction</title><p>By measuring the slopes of the initial tangent to the absorbance-time curves and</p><p>getting the linear range from each curve to determine the slope, the initial rate constant (K) of the reaction was identified from the absorbance-time plot under the most favorable conditions. In four experiments with various concentration of Cr<sup>3+</sup> prepared in 50 mL volumetric flasks between (1.1 &#215; 10<sup>−3</sup> - 1.6 &#215; 10<sup>−2</sup>) M, the measured absorbance at 373 nm increased as a function of time, and the limiting logarithm absorbance versus the time plots were constructed under the the best possible conditions.</p><p>For each curve, the slope, which corresponds to the reaction’s initial rate constant (k), was calculated at various concentrations, as shown in <xref ref-type="table" rid="table4">Table 4</xref>. The following equation was used to estimate the reaction’s order:</p><p>L o g K = log k ′ + n log C</p><p>where K is the initial rate of the reaction, C is the molar concentration of Cr<sup>3+</sup>, n is the order of the reaction, and k' is the apparent rate constant. The linear regression equation is: LogK = 1.0182x − 0.0574 with R<sup>2</sup> = 0.9868, the slope value which is n is 1.0182 (≈1) therefore confirming that the order of the reaction is the first one. The experimental K values were utilized to plot the linear curve; logK vs logC as shown in <xref ref-type="fig" rid="fig12">Figure 12</xref>. The data analysis was carried out with a 95% level of confidence; the standard errors of the slope and intercept are 0.0648 and 0.1535, respectively [<xref ref-type="bibr" rid="scirp.120878-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.120878-ref20">20</xref>].</p></sec><sec id="s3_11_2"><title>3.11.2. The Fixed-Time Method</title><p>At various Cr<sup>3</sup><sup>+</sup> concentrations, the reaction’s rate was calculated by measuring the absorbance at a predetermined fixed time that was precisely calculated [<xref ref-type="bibr" rid="scirp.120878-ref20">20</xref>]. As shown in <xref ref-type="table" rid="table5">Table 5</xref>, calibration curves of absorbance (ΔA) vs initial Cr<sup>3</sup><sup>+</sup></p><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Initial rate of reaction at different concentrations of Cr<sup>3+</sup> Ninhydrin = 0.0024 M and 0.0089 M KOH at room temperature</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >[Cr<sup>3</sup><sup>+</sup>] mol/L</th><th align="center" valign="middle" >Regression equation</th><th align="center" valign="middle" >Initial rate reaction (k)</th><th align="center" valign="middle" >logCr<sup>3</sup><sup>+</sup></th><th align="center" valign="middle" >Logk</th></tr></thead><tr><td align="center" valign="middle" >0.0011</td><td align="center" valign="middle" >y = −0.0008x + 0.1023 R<sup>2</sup> = 0.9552</td><td align="center" valign="middle" >8 &#215; 10<sup>−3</sup></td><td align="center" valign="middle" >−2.96</td><td align="center" valign="middle" >−3.09</td></tr><tr><td align="center" valign="middle" >0.004</td><td align="center" valign="middle" >y = −0.0075x + 0.3375 R<sup>2</sup> = 0.9549</td><td align="center" valign="middle" >7.5 &#215; 10<sup>−3</sup></td><td align="center" valign="middle" >−2.40</td><td align="center" valign="middle" >−2.12</td></tr><tr><td align="center" valign="middle" >0.008</td><td align="center" valign="middle" >y = −0.0078x + 0.6436 R<sup>2</sup> = 0.9295</td><td align="center" valign="middle" >7.8 &#215; 10<sup>−3</sup></td><td align="center" valign="middle" >−2.10</td><td align="center" valign="middle" >−2.10</td></tr><tr><td align="center" valign="middle" >0.012</td><td align="center" valign="middle" >y = −0.0087x + 0.9542 R<sup>2</sup> = 0.892</td><td align="center" valign="middle" >8.7 &#215; 10<sup>−3</sup></td><td align="center" valign="middle" >−1.92</td><td align="center" valign="middle" >−2.06</td></tr><tr><td align="center" valign="middle" >0.016</td><td align="center" valign="middle" >y = −0.0142x + 1.1707 R<sup>2</sup> = 0.9886</td><td align="center" valign="middle" >1.42 &#215; 10<sup>−2</sup></td><td align="center" valign="middle" >−1.80</td><td align="center" valign="middle" >−1.84</td></tr></tbody></table></table-wrap><table-wrap id="table5" ><label><xref ref-type="table" rid="table5">Table 5</xref></label><caption><title> Regression equations for Cr<sup>3+</sup> ions over range (1.1 &#215; 10<sup>−3</sup> - 1.6 &#215; 10<sup>−2</sup>) M at room temperature</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >ΔA</th><th align="center" valign="middle" >Time interval (min)</th><th align="center" valign="middle" >Regression equation</th><th align="center" valign="middle" >Correlation coefficient (R<sup>2</sup>)</th></tr></thead><tr><td align="center" valign="middle" >A4 - A2</td><td align="center" valign="middle" >2 - 4</td><td align="center" valign="middle" >y = 3.5089x − 0.0034</td><td align="center" valign="middle" >0.794</td></tr><tr><td align="center" valign="middle" >A6 - A2</td><td align="center" valign="middle" >2 - 6</td><td align="center" valign="middle" >y = 4.6634x − 0.0041</td><td align="center" valign="middle" >0.7724</td></tr><tr><td align="center" valign="middle" >A8 -A2</td><td align="center" valign="middle" >2 - 8</td><td align="center" valign="middle" >y = 7.4594x − 0.0067</td><td align="center" valign="middle" >0.8962</td></tr><tr><td align="center" valign="middle" >A10 - A2</td><td align="center" valign="middle" >2 - 10</td><td align="center" valign="middle" >y = 6.8909x + 0.002</td><td align="center" valign="middle" >0.8255</td></tr><tr><td align="center" valign="middle" >A12 - A2</td><td align="center" valign="middle" >1 - 12</td><td align="center" valign="middle" >y = 7.9068x + 0.0242</td><td align="center" valign="middle" >0.7553</td></tr><tr><td align="center" valign="middle" >A14 - A2</td><td align="center" valign="middle" >2 - 14</td><td align="center" valign="middle" >y = 10.104x + 0.0043</td><td align="center" valign="middle" >0.9131</td></tr><tr><td align="center" valign="middle" >A16 - A2</td><td align="center" valign="middle" >2 - 16</td><td align="center" valign="middle" >y = 11.495x + 0.0173</td><td align="center" valign="middle" >0.8976</td></tr><tr><td align="center" valign="middle" >A18 - A2</td><td align="center" valign="middle" >2 - 18</td><td align="center" valign="middle" >y = 12.687x + 0.0277</td><td align="center" valign="middle" >0.8465</td></tr><tr><td align="center" valign="middle" >A20 - A2</td><td align="center" valign="middle" >2 - 20</td><td align="center" valign="middle" >y = 23.097x − 0.0325</td><td align="center" valign="middle" >0.8131</td></tr></tbody></table></table-wrap><p>concentration were created at specified intervals of 2, 4, 6, 8, 10, 12, 14, 16, and 20 min (5).</p><p>From this table it can be conclude that the best time for measurement is at the time A14-A2 because at this interval the R<sup>2</sup> is 0.913 which is the highest, also we can consider the slope which represent the molar absorptivity, the time interval A20-A2 is also can be applied because it has the higher molar absorptivity.</p></sec></sec></sec><sec id="s4"><title>4. Conclusion</title><p>In this research, a new spectrophotometric method for the determination of Cr (III) using ninhydrin was investigated. Ninhydrin in this research acts as chromogenic agent. The ability of ninhydrin (a bidentate ligand) to function as an analytical reagent was the subject of some interesting and practical data presented in this work. The chromogenic reagent in this procedure was ninhydrin. This technique does not require strict requirements to generate stable colored complex which measured at λ<sub>max</sub> = 375 nm under variable conditions. Also the experimental results showed that this method is reliable, simple, sensitive, and reproducible for the determination of chromium ions in low concentrations utilizing the inexpensively available ninhydrin. The calibration curve was constructed under optimum conditions. This method has large calibration sensitivity with low values of LOD and LOL and wide working range. Kinetic studies are investigated and the validity is applied. The inter-day and intra-day experiments under the optimum conditions were studied also and the validity was tested.</p></sec><sec id="s5"><title>Acknowledgements</title><p>The Deanship of Graduate Studies at Al Al-Bayt University (Mafraq/Jordan), which provided financial support, is acknowledged by the authors.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Baker, H.M., Rahoomi, T.D. and Abdel-Halim, H. (2022) Spectrophotometric Method for Determination of Chromium Ion in Aqueous Solution Using Ninhydrin. American Journal of Analytical Chemistry, 13, 382-398. https://doi.org/10.4236/ajac.2022.1310026</p></sec><sec id="s8"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.120878-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">El-Enany, N., Belal, F. and Rizk, M. (2002) A Simple Kinetic Spectrophotometric Method for the Determination of Isoxsuprine in Dosage Forms. Il Farmaco, 57, 641-648. https://doi.org/10.1016/S0014-827X(02)01236-3</mixed-citation></ref><ref id="scirp.120878-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Narayana, B., Ashwini, K., Narayana, S.D. and Veena, K. (2010) Spectrophotometric Determination of Ranitidine Hydrochloride Based on the Reaction with p-Dimethylaminobenzaldehyde. 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