『Abstract
Environmentally significant phosphorus species in water and phosphorus
fractions in sediments are briefly discussed and the methods for
their determination are described. One of the most critical analytical
steps is the separation of the different forms which, after conversion
into orthophosphates, may be determined by a multitude of various
techniques. spectrophotometric methods are often preferred for
routine analysis. Several rapid automatic methods for the separation
and determination of orthophosphate, linear polyphosphates, cyclic
condensed phosphates and lower oxidation state anions of phosphates,
which may exist in natural and waste waters, have been developed.
They are mainly based on the use of flow-injection analysis, high-performance
liquid chromatography, including ion chromatography, capillary
electrophoresis and a few other techniques. These methods have
been described and critically evaluated.』
Introduction
Water analysis
Particulate phosphorus forms
Determination of phosphorus fractions in sediments
References
Particulate |
Total suspended phosphorus Suspended reactive phosphorus Suspended acid-hydrolysable phosphorus Suspended organic phosphorus |
Dissolved |
Total dissolved phosphorus Dissolved reactive phosphorus Dissolved acid-hydrolysable phosphorus Dissolved organic phosphorus |
Formula | Abbreviation | Name of anion |
H3PO4 | P1 | Orthophosphate |
Polyphosphates (linear condensed phosphates) Hn+2PnO3n+1 | ||
H4P2O7 | P2 | Diphosphate |
H5P3O10 | P3 | Triphosphate |
H6P4O13 | P4 | Tetraphosphate |
Cyclic condensed phosphates (metaphosphates) (HPO3)n | ||
H3P3O9 | P3m | Trimetaphosphate |
H4P4O12 | P4m | Tetrametaphosphate |
Lower oxidation states | ||
H3PO2 | P1 | Phosphinate |
H3PO3 | P3 | Phosphonate |
H4P2O6 | P4-P4 | Hypophosphate |
H4P2O7 | P3-O-P3 | Diphosphonate |
H4P2O6 | P3-O-5 | Isohypophosphate |
Technique |
Detection limit (μg/L) |
Sample |
Spectrophotometry (SP) | 1-100 | River water |
2-5 | Tap water | |
0.005* | Sea and lake waters | |
0.1-400 | Natural and tap waters | |
X-ray fluorescence analysis (XRFA) | 0.03* | River water |
0.006* | Nastural waters | |
Flame photometry | 30 | Tap, river and lake waters |
Voltammetry | 1-3 | Natural and waste waters |
Amperometric titration | 2000 | Natural waters |
Potentiometric titration | 40 | Natural waters |
Inductively coupled plasma atomic emission spectroscopy (ICP-AES) | 1-20 | Natural waters |
|
River and sea waters | |
Inductively coupled plasma mass spectrometry | 40 | Natural waters |
Electrothermal vaporization | 0.3 | Natural waters |
Molecular fluorimetry | 2-20 | Natural and tap waters |
Ion chromatography | 10 | Natural and tap waters |
Liquid chromatography-SP | 10 | Natural waters |
Flow-injection analysis (FIA)-SP | 0.1-12 | Natural waters |
* After preconcentration. |
Method | Concentration range (μg/L) |
Vanadomolybdophosphoric acid | 0.1-20 |
Stannous chloride | 0.007-2.0 |
Ascorbic acid | 0.01-2.0 |
Phosphorus fraction | Significance | |
1. | Total phosphorus | Indivative of total phosphorus burden |
2. | Adsorbed phosphorus | Easily available fraction |
3. | Non-apatitic phosphorus | Available phosphorus fraction in oxugen absence |
4. | Apatitic phosphorus | Relatively stable and inert phosphorus fraction |
5. | Organic phosphorus | Slowly but continuously available fraction |
6. | Residual phosphorus | Not available under environmental conditions |