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Ohta and Tanaka reported on an ion-exchange chromatographic method for the simultaneous analysis of several inorganic anions and the cations \(\mathrm{Mg}^{2+}\) and \(\mathrm{Ca}^{2+}\) in water. \({ }^{28}\) The mobile phase includes the ligand 1,2,4 -benzenetricarboxylate, which absorbs strongly at \(270 \mathrm{nm}\). Indirect detection of the analytes is possible because its absorbance decreases when complexed with an anion. (a) The procedure also calls for adding the ligand EDTA to the mobile phase. What role does the EDTA play in this analysis? (b) A standard solution of \(1.0 \mathrm{mM} \mathrm{NaHCO}_{3}, 0.20 \mathrm{mM} \mathrm{NaNO}_{2}, 0.20\) \(\mathrm{mM} \mathrm{MgSO}_{4}, 0.10 \mathrm{mM} \mathrm{CaCl}_{2},\) and \(0.10 \mathrm{mM} \mathrm{Ca}\left(\mathrm{NO}_{3}\right)_{2}\) gives the following peak areas (arbitrary units). \(\begin{array}{lcccc}\text { ion } & \mathrm{HCO}_{3}^{-} & \mathrm{Cl}^{-} & \mathrm{NO}_{2}^{-} & \mathrm{NO}_{3}^{-} \\ \text {peak area } & 373.5 & 322.5 & 264.8 & 262.7 \\\ \text { ion } & \mathrm{Ca}^{2+} & \mathrm{Mg}^{2+} & \mathrm{SO}_{4}^{2-} & \\\ \text { peak area } & 458.9 & 352.0 & 341.3 & \end{array}\) Analysis of a river water sample (pH of 7.49 ) gives the following results. \(\begin{array}{lcccc}\text { ion } & \mathrm{HCO}_{3}^{-} & \mathrm{Cl}^{-} & \mathrm{NO}_{2}^{-} & \mathrm{NO}_{3}^{-} \\ \text {peak area } & 310.0 & 403.1 & 3.97 & 157.6 \\ \text { ion } & \mathrm{Ca}^{2+} & \mathrm{Mg}^{2+} & \mathrm{SO}_{4}^{2-} & \\ \text { peak area } & 734.3 & 193.6 & 324.3 & \end{array}\) Determine the concentration of each ion in the sample. (c) The detection of \(\mathrm{HCO}_{3}^{-}\) actually gives the total concentration of carbonate in solution \(\left(\left[\mathrm{CO}_{3}^{2-}\right]+\left[\mathrm{HCO}_{3}^{-}\right]+\left[\mathrm{H}_{2} \mathrm{CO}_{3}\right]\right) .\) Given that the \(\mathrm{pH}\) of the water is \(7.49,\) what is the actual concentration of \(\mathrm{HCO}_{3}^{-}\) ? (d) An independent analysis gives the following additional concentrations for ions in the sample: \(\left[\mathrm{Na}^{+}\right]=0.60 \mathrm{mM} ;\left[\mathrm{NH}_{4}^{+}\right]=0.014\) \(\mathrm{mM}\); and \(\left[\mathrm{K}^{+}\right]=0.046 \mathrm{mM}\). A solution's ion balance is defined as the ratio of the total cation charge to the total anion charge. Determine the charge balance for this sample of water and comment on whether the result is reasonable.

Short Answer

Expert verified
EDTA prevents metal ion interference; calculate each ion's sample concentration using peak areas and standard values; use pH to find true \( \text{HCO}_3^- \) concentration; ion balance confirms sample consistency.

Step by step solution

01

Understanding the role of EDTA

EDTA is a chelating agent that binds strongly to metal ions such as \( \text{Mg}^{2+} \) and \( \text{Ca}^{2+} \). In the context of ion-exchange chromatography, EDTA is added to the mobile phase to prevent these metal ions from interacting with the stationary phase, which can interfere with the detection of the anions. By forming stable complexes with these metal ions, EDTA ensures more reliable anion detection and prevents peak broadening.
02

Calculating concentration of ions in standard solution

Use the relationship between peak area and concentration. The formula for ion concentration based on peak areas compared to the standard is:\[C_{\text{sample}} = \frac{\text{Peak Area}_{\text{sample}}}{\text{Peak Area}_{\text{standard}}} \times C_{\text{standard}}\]Apply this formula for each ion to find their concentrations in the river water sample. For example, for \( \text{HCO}_3^- \):\[C_{\text{HCO}_3^-} = \frac{310.0}{373.5} \times 1.0 \, \text{mM}\]
03

Calculating carbonate species concentration

To find the concentration of \( \text{HCO}_3^- \), use the pH value and the equilibrium expressions for carbonate species. At pH 7.49, most total carbonate is as \( \text{HCO}_3^- \), but a small fraction will be \( \text{CO}_3^{2-} \) and \( \text{H}_2\text{CO}_3 \). Use the Henderson-Hasselbalch equation to adjust the concentration:\[pK_a1 = 6.35, \, pK_a2 = 10.33, \, ext{use ratios to find distribution}\]
04

Charge balance calculation

First, calculate the charge contributed by each ion in the sample using their concentration and charge magnitude. Then, sum the total positive and negative charges. The ion balance is:\[\text{Ion Balance} = \frac{\sum \text{Cations} \times \text{Charge}}{\sum \text{Anions} \times \text{Charge}}\]Substitute known concentrations for ions like \( \text{Na}^+ \), \( \text{NH}_4^+ \), \( \text{K}^+ \), \( \text{HCO}_3^- \), \( \text{Cl}^- \), \( \text{NO}_2^- \), etc.

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Key Concepts

These are the key concepts you need to understand to accurately answer the question.

Ion detection
In ion-exchange chromatography, ion detection is a critical step that allows for the identification and quantification of ions in a solution. The method relies on the indirect detection of analytes by measuring changes in the absorbance of a substance within the mobile phase. Typically, the ligand used in the process, such as 1,2,4-benzenetricarboxylate, absorbs light at a specific wavelength—in this case, at 270 nm. When anions in the sample interact with the ligand, this interaction alters the absorbance, leading to indirect detection. The resultant absorbance drop correlates with the presence and concentration of the specific anions being analyzed. By comparing these absorbance changes to those from known standards, the concentrations of the ions in the sample can be determined.
EDTA role in chromatography
The use of EDTA in ion-exchange chromatography is crucial due to its chelating properties. EDTA is a well-known agent that strongly binds to various metal ions, including calcium (\(\text{Ca}^{2+}\)) and magnesium (\(\text{Mg}^{2+}\)). During the chromatographic process, these metal ions could otherwise interact with the stationary phase, potentially interfering with the detection of anions and causing broader peaks and less defined chromatographic results. By adding EDTA to the mobile phase, metal ions are bound tightly, preventing such interactions. This not only enhances the reliability of anion detection by stabilizing the system but also helps in maintaining sharp and accurate chromatographic peaks, facilitating better identification and quantification of analytes.
Charge balance calculation
Calculating the charge balance in a solution involves evaluating the total charges contributed by both cations and anions. In a balanced solution, the total positive charge from cations should equal the total negative charge from anions. Calculating this involves:
  • Summing up the products of the concentration and charge for each cation and anion.
  • Checking if the ratios of these sums approach an equal value, meaning a balanced charge distribution.
To calculate the ion balance as given in the exercise, you simply use the formula:\[\text{Ion Balance} = \frac{\sum \text{Cation Concentrations} \times \text{Charges}}{\sum \text{Anion Concentrations} \times \text{Charges}}\]This calculation helps in verifying the accuracy of your analysis since any significant deviation from unity might indicate errors in concentration determination or contamination in the sample.
Concentration determination
Determining ion concentration in a sample using ion-exchange chromatography involves comparing the peak areas obtained from the sample to those from a known standard. This is done using a simple ratio formula:\[C_{\text{sample}} = \frac{\text{Peak Area}_{\text{sample}}}{\text{Peak Area}_{\text{standard}}} \times C_{\text{standard}}\]This equation forms the basis of quantifying ions, as it relies on peak area values that correspond to the concentration of ions. It's important to analyze each ion separately. By applying this formula across all ions of interest, such as bicarbonate (\(\text{HCO}_3^-\)), chloride (\(\text{Cl}^-\)), and others in the sample, precise concentrations can be calculated, allowing for a comprehensive understanding of the sample's ion composition.

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Most popular questions from this chapter

A series of polyvinylpyridine standards of different molecular weight was analyzed by size-exclusion chromatography, yielding the following results. \begin{tabular}{cc} formula weight & retention volume (mL) \\ \hline 600000 & 6.42 \\ 100000 & 7.98 \\ 20000 & 9.30 \\ 3000 & 10.94 \end{tabular} When a preparation of polyvinylpyridine of unknown formula weight is analyzed, the retention volume is \(8.45 \mathrm{~mL}\). Report the average formula weight for the preparation.

A mixture of \(n\) -heptane, tetrahydrofuran, 2 -butanone, and \(n\) -propanol elutes in this order when using a polar stationary phase such as Carbowax. The elution order is exactly the opposite when using a nonpolar stationary phase such as polydimethyl siloxane. Explain the order of elution in each case.

Bohman and colleagues described a reversed-phase HPLC method for the quantitative analysis of vitamin \(\mathrm{A}\) in food using the method of standard additions. \({ }^{27}\) In a typical example, a \(10.067-\mathrm{g}\) sample of cereal is placed in a 250 -mL Erlenmeyer flask along with \(1 \mathrm{~g}\) of sodium ascorbate, \(40 \mathrm{~mL}\) of ethanol, and \(10 \mathrm{~mL}\) of \(50 \% \mathrm{w} / \mathrm{v} \mathrm{KOH}\). After refluxing for \(30 \mathrm{~min}, 60 \mathrm{~mL}\) of ethanol is added and the solution cooled to room temperature. Vitamin \(\mathrm{A}\) is extracted using three \(100-\mathrm{mL}\) portions of hexane. The combined portions of hexane are evaporated and the residue containing vitamin A transferred to a \(5-\mathrm{mL}\) volumetric flask and diluted to volume with methanol. A standard addition is prepared in a similar manner using a \(10.093-\mathrm{g}\) sample of the cereal and spiking with \(0.0200 \mathrm{mg}\) of vitamin \(\mathrm{A}\). Injecting the sample and standard addition into the HPLC gives peak areas of, respectively, \(6.77 \times 10^{3}\)and \(1.32 \times 10^{4}\). Report the vitamin \(\mathrm{A}\) content of the sample in milligrams/100 g cereal.

The analysis of \(\mathrm{NO}_{3}^{-}\) in aquarium water is carried out by CZE using \(\mathrm{IO}_{4}^{-}\) as an internal standard. A standard solution of \(15.0 \mathrm{ppm} \mathrm{NO}_{3}^{-}\) and 10.0 ppm \(\mathrm{IO}_{4}^{-}\) gives peak heights (arbitrary units) of 95.0 and 100.1 , respectively. A sample of water from an aquarium is diluted 1: 100 and sufficient internal standard added to make its concentration \(10.0 \mathrm{ppm}\) in \(\mathrm{IO}_{4}^{-}\). Analysis gives signals of 29.2 and 105.8 for \(\mathrm{NO}_{3}^{-}\) and \(\mathrm{IO}_{4}^{-},\) respectively. Report the \(\mathrm{ppm} \mathrm{NO}_{3}^{-}\) in the sample of aquarium water.

Haddad and associates report the following retention factors for the reversed- phase separation of salicylamide and caffeine. \({ }^{25}\) \(\begin{array}{ccccccc}\% \text { methanol } & 30 \% & 35 \% & 40 \% & 45 \% & 50 \% & 55 \% \\ k_{\text {sal }} & 2.4 & 1.6 & 1.6 & 1.0 & 0.7 & 0.7 \\\ k_{\text {caff }} & 4.3 & 2.8 & 2.3 & 1.4 & 1.1 & 0.9\end{array}\) (a) Explain the trends in the retention factors for these compounds. (b) What is the advantage of using a mobile phase with a smaller \(\% \mathrm{v} / \mathrm{v}\) methanol? Are there any disadvantages?

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