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Trace Total Mercury Analysis
Mercury Speciation of River Water
Mercury Speciation of Lake Water
Mercury Speciation of Soil
Mercury Speciation of Tissue
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Trace Total Mercury Analysis Mercury Speciation of River Water Mercury Speciation of Lake Water Mercury Speciation of Soil Mercury Speciation of Tissue |


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The
movement of “zero tolerance” arsenic and selenium associated with
drinking water, wastewater, soil, and groundwater regulatory limits
necessitates the demand for absolute results. Most analytical
techniques applied for arsenic and selenium analysis retain inherent
interferences which can often bias results, especially at lower
concentrations. Therefore, Applied Speciation employ
state-of-the-art methods and instrumentation to surpass current and
prospective demands for trace arsenic and selenium analysis.
In the recent years, inductively coupled plasma mass spectrometry
(ICP-MS) became one of the most common detectors for the
determination of trace metals in environmental samples. While ICP-MS
can be used to determine most analytes of environmental concern at
ppt levels, conventional ICP-MS instruments can suffer from various
issues making trace analysis of arsenic and selenium very difficult.
By utilizing the DRC technology with the methods developed at ASC,
detection limits in the range of 10 ng/L (ppt) for Arsenic and
Selenium can be achieved easily with negligible bias.
Comparison between HG-AAS/AFS and ICP-DRC-MS
Hydride generation atomic absorption spectrometry and atomic
fluorescence spectrometry (HG-AAS and HG-AFS, respectively)
facilitates the reaction of sodium borohydride with reduced arsenic
and selenium species (arsenite and selenite) to produce volatile
hydrides which are purged from solution and detected
spectrophotometrically. While these methods can produce very low
detection limits (20-500 ng/L), they are prone to severe matrix
interferences. The major issue with hydride generation methods is
that they are operationally limited to the quantification of
arsenite and selenite in solution; requiring pretreatment to convert
all arsenic and selenium species to arsenite and selenite before
analysis. Due to this inherent limitation, these methods can only
provide “total reducible” arsenic and selenium and not “total”
results that ICP-MS can provide. In addition, the complexity of the
sample matrix can alter the efficiency of the reduction procedure or
the hydride generation reaction. The interferences from transition
metals, dissolved organic carbon, and salinity are very well
documented and allow for significant biases associated with complex
matrices, especially at trace levels.
Finally, the tedious sample preparation protocols necessitate
commercial laboratories to charge significantly more for this
analysis compared to ICP-DRC-MS analysis.
Conclusion
ICP-DRC-MS provides interference elimination and robustness for true
total arsenic and selenium analysis in any matrix. The method offers
better quality data than hydride generation methods and provide
significant reduction in analytical costs. The same technology can
also be used for other analytes such as chromium, iron, cadmium,
etc.
Also see the following Application Notes:
Total Arsenic and Arsenic Speciation in Human Biological Samples
(pdf)
Arsenic Speciation in Soils and Sediments (pdf)
Arsenic
Speciation in Blood
Determination of Selenium in FGD Wastewaters
Our scientists have tremendous experience with trace analysis. If
you have any questions or would like a quotation, please feel free
to email us at info@appliedspeciation.com or call
(425) 483-3300 .
Feel free to visit our website on a regular basis as we will be
providing scientific discussions and useful links to save you time
and money.
Applied Speciation and Consulting 2009