alexa
Reach Us +447482877761
Effect of Heating on the Color Formation Reaction in the Murphy and Riley Method for the Determination of Phosphate in Natural Waters | OMICS International
ISSN: 2380-2391
Journal of Environmental Analytical Chemistry
Make the best use of Scientific Research and information from our 700+ peer reviewed, Open Access Journals that operates with the help of 50,000+ Editorial Board Members and esteemed reviewers and 1000+ Scientific associations in Medical, Clinical, Pharmaceutical, Engineering, Technology and Management Fields.
Meet Inspiring Speakers and Experts at our 3000+ Global Conferenceseries Events with over 600+ Conferences, 1200+ Symposiums and 1200+ Workshops on Medical, Pharma, Engineering, Science, Technology and Business

Effect of Heating on the Color Formation Reaction in the Murphy and Riley Method for the Determination of Phosphate in Natural Waters

Su-Cheng Pai1*, Tzu-Yuan Wang1, Tien-Hsi Fang2 and Kuo-Tung Jiann3

1Institute of Oceanography, National Taiwan University, Taipei, Taiwan

2Department of Marine Environmental Informatics, National Taiwan Ocean University, Keelung, Taiwan

3Department of Oceanography, National Sun Yat-Sen University, Kaohsiung, Taiwan

*Corresponding Author:
Su-Cheng Pai
Institute of Oceanography
National Taiwan University
Taipei, Taiwan
Tel: 886922227358
E-mail: [email protected]

Received date: April 30, 2015; Accepted date: May 12, 2015; Published date: May 20, 2015

Citation: Pai S, Wang T, Fang T, Jiann K (2015) Effect of Heating on the Color Formation Reaction in the Murphy and Riley Method for the Determination of Phosphate in Natural Waters. J Environ Anal Chem 2:139. doi: 10.4172/2380-2391.1000139

Copyright: © 2015 Pai S et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

Visit for more related articles at Journal of Environmental Analytical Chemistry

Abstract

Heating is frequently applied to enhance the reaction rate for the determination of phosphate but it may cause unexpected errors. Experiments show that the spectrum of the blue color produced by the Murphy and Riley method is subject to change at different temperatures. The variation of the molar extinction coefficient at 880 nm was found to be -48 M-1cm-1°C-1, or a relative trend of -0.22 % °C-1 w.r.t. to the absorbance at 30°C. When the color formation reaction took place at >35°C, the absorbance started to climb. At temperatures >60°C, the results were erratic and the change becomes irreversible. These findings suggest that the measurement should be made at room temperature and any heating process above 35°C should be avoided. A thermostated cuvette holder set at 30°C is highly recommended for both manual and flow type operation.

Keywords

Phosphate; Spectrum; Heating; Color formation reaction

Introduction

The molybdate-ascorbic acid method developed by Murphy and Riley [1] for the determination of phosphate in natural waters has been widely adopted in many scientific disciplines [2-4]. When the manual procedure is converted to an automated operation, heating is frequently applied to enhance the rate of color formation reaction for a fast throughput. For example, APHA/AWWA/WEF Standard Methods have suggested an on-line 37°C water bath [5]; Johnson and Petty [6] have employed a 50°C bath; and in an extreme case, a 95°C reactor has been used by Yuchi et al. [7]. Although heating can effectively improve the reaction rate [8,9], some scientists have encountered other problems. Benson et al. [10] have reported a phenomenon where the peak signals decreased significantly when the bath temperature was raised up to 60°C; Drummond and Maher [11] and Zhang et al. [12] have both observed noticeable silicate interferences at elevated temperatures. They have suggested that the determination should be preferably performed at room temperature.

However, we have encountered a dilemma on whether or not one should apply an on-line heating device. On our past expedition cruises, seawater samples were collected from different depths (e.g. from surface to >3000 m deep with original temperatures from 30°C down to 2°C) and all nutrients including phosphate were measured on-board by a flow injection system within 1 hour after retrieving the sampler to the deck. The use of an on-line heating bath could largely minimize the large temperature differences between samples and standards, but the uncertainty induced has yet been well evaluated. In order to clarify this problem, a series of heating experiment was carried out at higher concentrations (30-50 μM) in order to magnify the variation. The results will provide field analysts a quantified measure of the heating effect so they are able to choose a proper way to avoid such an uncertainty.

Materials and Methods

Reagents

Mixed reagent (HMoSb): A 200 mL molybdate solution (containing 5.1 g of ammonium molybdate heptahydrate) was poured gradually while stirring into a beaker filled with 180 mL of conc. sulfuric acid, followed by mixing a 100 mL of the antimony solution (containing 0.5 g of potassium antimony tartrate). The final volume was made up to 500 mL.

Ascorbic acid reagent (ASC): An amount of 13.2 g of L-ascorbic acid was dissolved in 250 mL of double distilled water.

Phosphate standard: A 10 mM P stock solution was prepared by dissolving 0.1361 g of KH2PO4 in 1 L of double distilled water. Diluted working standards were prepared from this stock solution.

Spiked seawater: A filtered surface seawater (salinity=33.4 psu) was prepared previously. The original concentration was <0.05 μΜ P. An aliquot of 3 mL of the stock standard solution was added to this seawater to make a final volume of 1 L to give a spiking concentration of 30 μΜ.

Reagent strengths: The reagent strengths used in this study were slightly different from the original recipe [1] with a lower acidity to minimize Si interference and higher Sb3+ and ASC concentrations to increase the reaction rate [11,12]. When 2 mL of HMoSb reagent and 1 mL of ASC reagent are added to a 25 mL aliquot of sample, the final reagent strengths are: [Mo]=4.13 mM; [H+]=309 mM; [Sb3+]=0.213 mM; [ASC]=10.7 mM, with a [H+]/[Mo] ratio of 74.8.

Apparatus

A Shimadzu UV1800 spectrophotometer was equipped with a temperature-controlled cuvette holder (Shimadzu T-83400-52) connected to a thermostat water circulation bath (Firstek B401H) with a 1 kW heater and a 700 W cooler (Figure 1). A dome-type flow cuvette (Hellma, 1 cm length, 450 μL capacity) was used. The sample solution was placed in a reaction bottle immersed in a second thermostat water bath (Firstek B206) and controlled by a 750 W heater. The sample could be quickly taken up by a peristaltic pump to fill up the cuvette in 10 s.

environmental-analytical-chemistry-Apparatus-monitor-color

Figure 1: Apparatus used to monitor the color formation reaction in this study. The system has two thermostat baths (#1 and #2). The first one is connected to a water-circulating cuvette holder installed in a Shimadzu UV1800 spectrophotometer. A dome-type Hellma flow cuvette (1 cm, 450 μL)is inserted into the holder. The sample is placed in a bottle immersed in a second thermostat. Upon adding reagents, the mixture is quickly taken up to fill the cuvette by a peristaltic pump at a rate of 20 mL min-1.

Experiment designs

Exp-1 Absorption spectra: A fully-developed blue color solution was transferred to the cuvette for scanning from 950 to 650 nm at different temperatures. The absorbance at 880 nm was recorded along a time scale while the thermostat was heated up step-wisely from 15 to 90°C, then cooled back down to 15°C.

Exp-2 Color formation at fixed temperatures: Both thermostats were adjusted to the same temperature. The reagent added sample was immediately transferred to the flow cuvette then trapped for observation of the formation curve.

Exp-3 Color formation at elevating temperature: The starting temperature was set at 25°C but the cuvette holder was heated up to 30- 90°C at 15°C intervals. The sample added with reagents was transferred immediately to the heated flow cuvette. The color formation curve obtained this way was under a temperature-ramping condition.

Results and Discussion

Spectra at different temperatures

In Exp-1 two color-fully-developed phosphomolybdenum blue solutions (50 μΜ in freshwater and 30 μΜ in seawater) were scanned at different temperatures and the overlapped absorption spectra are shown in Figure 2. The change of spectra due to temperature was significant, and a knot at a wavelength of 935 nm was found for both media. On the left-hand side of this knot the absorption patterns became lower as temperature increased, and vice versa.

environmental-analytical-chemistry-Overlapped-spectra-phosphomolybdenum

Figure 2: Overlapped spectra of the phosphomolybdenum blue complex at various temperatures for (A) 50 μM P in freshwater and (B) 30 μM P in seawater. The temperature settings were 25, 35- 75 °C at 10°C intervals.

The observation on the effect of changing temperature to the molar extinction coefficient at 880 nm is shown in Figure 3. The blue colored solution was again transferred to fill the cuvette. The cuvette holder was first cooled down to 15°C, and then the thermostat was heated up in a step-wise manner at 5°C intervals. As temperature increased, the absorbance decreased like a mirror image. The molar extinction coefficient at 880 nm was found to be 23400, 22850, 22600, 21700 … 19800 M-1cm-1 at 15, 25, 30, 50 … 90°C, respectively. The slope of variation was found to be -48 M-1cm-1°C-1 (Figure 4) or a relative trend of -0.22 %°C-1 w.r.t. the absorbance value at 30°C. After reaching the highest 90°C, the cooler of the thermostat was switched on and the temperature was dropped also in a step-wise manner. At the ending 15°C the absorbance went back to almost the identical value as that of the starting 15°C. In the seawater medium the trend and slope were almost the same as that in freshwater. The change due to temperature variation was apparently reversible  in this experiment.

environmental-analytical-chemistry-Observation-absorbance-temperature

Figure 3: Observation of the variation of absorbance at 880 nm by changing the temperature of the cuvette holder. (A) 50 μM P in freshwater (B) 30 μM P in seawater.

environmental-analytical-chemistry-Relationship-molar-extinction

Figure 4: Relationship between the molar extinction coefficient (880 nm) and temperature in (circle) freshwater and (dot) seawater. The slope was found to be -48 M-1cm-1°C-1 for both media, or a relative trend of -0.22%°C-1 with respect to 22600 M-1cm-1 at 30 °C.

Color formation reaction at fixed temperatures

In Exp-2 the color formation reaction took place at fixed temperatures (20, 25, 30, 35 and 45°C) and the results are presented in Figure 5. At 20°C the curve was an “S” shape with a slow beginning, followed by an accelerating stage and then a slow ending. The time for reaching 90% of maximum absorbance (t90%) was 62 s at 20°C, reduced to 38 and 24 s at 25 and 30°C, with -1% and -2% lower absorbances. At 45°C, the reaction was very fast (t90%<15s), but the ending absorbance appeared to have a rising trend. This rising phenomenon can be more clearly seen in the enlarged diagrams in Figure 6 and was not found to be due to the change of the reagent blank (all reagent blanks were <0.001 at 10 min).

environmental-analytical-chemistry-formation-reaching-absorbance

Figure 5: (Left) The color formation curves for a 10 μM P solution at 20, 25, 30, 35 and 45°C, respectively. (Right) Time required for reaching 90% of maximum absorbance (t90%) is a function of temperature.

environmental-analytical-chemistry-Enlarged-curves-temperatures

Figure 6: (Left) Enlarged color formation curves of different P concentrations and at various fixed temperatures. (Right) Absorbance at 400 s as a function of temperature. Arrows indicate the consistent climbing-up of the reading. Dash lines indicate a trend of -0.22%°C-1. Aliquots of 25 ml of spike samples were added with 3 ml of reagents to give final concentrations of (A) 8.93 μM P (B) 26.8 μM P (C) 44.6 μM P in freshwater and (D) 26.8 μM P in seawater.

There are four samples shown in Figure 6 with three tested concentrations (10, 30 and 50 μΜ P) in freshwater and the last one was 30 μΜ P in seawater. At 45°C the absorbance for a 10 μΜ P sample was 0.198 at 30 s and rose to 0.204 at 400 s, with a difference as large as +3% or a slope of +0.5%min-1. This climbing trend continued even after 400 s, and the slope was more obvious at the relatively low concentration comparing to +0.25%min-1 at 30 μΜ and +0.16%min-1 at 50 μΜ, respectively. For the seawater medium, the phenomenon was almost the same as for freshwater. It reveals that, the molecular structure of the blue complex might be different if the reaction takes place at a temperature higher than 35°C. Exp-2 did not continue to add higher temperatures as water vapor started to condense on the wall of the sample bottle.

Reaction at ramped temperatures

In Exp-3 the sample (50 μΜ P) was maintained at a fixed starting temperature of 25°C and the cuvette holder was heated up by setting the thermostat at 30, 45, 60, 75 and 90°C, respectively. The results were somewhat erratic. All curves shown in Figure 7 tangle with each other in the first hour and the readings appear to stabilize only after 180 min. Enlarged diagram (Figure 7) gives a clearer pattern. Only at 30°C is the curve in a normal shape. At 45°C the blue color formed quickly in 30 s, but dropped a little afterward, and then rose again gradually after 3 min. At 60°C the curve dropped after 30 s, rose after 2 min. At 75°C the amplitude of the drop-rise became magnified, and after 15 min the absorbance dropped again. At 90°C the curve ran high quickly to an absorbance of 1.2 at 7 min which was +20% in excess of the normal reading. After 7 min the absorbance dropped down gradually. The cause of this hump is unclear, and it is not parallel with the reagent blanks which became obvious only at > 75°C after 10 min. An extended observation was made by allowing the blue color to form at high temperatures and then cool down to 25°C. The final absorbance readings did go high but did not go back to the expected values as described in Exp-1. The effect of heating in Exp-3 was no longer reversible.

environmental-analytical-chemistry-Color-formation-curves

Figure 7: (Left) Color formation curves of a 50 μM P sample (final concentration 44.6 μM P) with a starting temperature of 25 °C and ending temperatures of 30, 45, 60, 75 and 90 °C, respectively. All curves were raw signals without deducting the reagent blanks. Reagent blanks were significant only when the temperature was higher than 75 °C and 10 min after the reaction began. (Right) Enlarged diagram showing the change in the first 10 min, with dash lines indicating the reagent blank-deducted curves.

Conclusion

The negative aspect of heating on the Murphy and Riley method for the determination of phosphate has long been overlooked by scientists but evidences found in this study reveals that the uncertainty induced by the temperature difference should not be ignored. In general, the molar extinction coefficient of the final blue color at 880 nm has an inverse relationship with temperature. If the color formation reaction takes place at temperatures much higher than 35°C, erratic results can happen and it is irreversible even if the solution cools back down to room temperature. The use of heating at more than 35°C should be avoided in any case. When a batch of samples having a wide temperature range is to be measured, or when a sample is just digested for total P measurement, they should be left to equilibrate with the surrounding temperature before adding reagents. For manual operation a temperature-controlled cuvette holder set at a fixed 30°C can be used for optimal precision and accuracy. For automated analysis the same cuvette holder can be used to reduce the possible variation due to the temperature effect.

Acknowledgements

The authors would like to thank B.W. Tang of Shih-Shin Instrument Co., Taipei, Taiwan for his suggestion on cuvette holder. This project was supported by the National Science Council, Taipei, Taiwan under a contract no. NSC-97-2611- M-002-002-MY3.

References

Select your language of interest to view the total content in your interested language
Post your comment

Share This Article

Article Usage

  • Total views: 12821
  • [From(publication date):
    June-2015 - Feb 21, 2020]
  • Breakdown by view type
  • HTML page views : 8968
  • PDF downloads : 3853
Top