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Related Concept Videos

Atomic Absorption Spectroscopy: Lab01:21

Atomic Absorption Spectroscopy: Lab

For AAS measurements, samples must be introduced as clear solutions, often requiring extensive preliminary treatment to dissolve materials like soils, animal tissues, and minerals. Common methods for sample preparation include treatment with hot mineral acids, wet ashing, combustion in closed containers, high-temperature ashing, or fusion with reagents.
 Solutions containing organic solvents, such as low-molecular-mass alcohols, esters, or ketones, enhance absorbances by increasing nebulizer...
Atomic Absorption Spectroscopy: Atomization Methods01:25

Atomic Absorption Spectroscopy: Atomization Methods

Atomic Absorption Spectroscopy (AAS) atomizes samples through flame atomization or electrothermal atomization. Flame atomization typically involves a nebulizer and spray chamber assembly to combine the sample with a fuel–oxidant mixture, creating a fine aerosol mist that enters a burner. Typically, the fuel and oxidant are combined in an approximately stoichiometric ratio. However, for atoms that are easily oxidized, a fuel-rich mixture may be more advantageous. Only about 5% of the aerosol...
Flame Photometry: Overview01:02

Flame Photometry: Overview

Flame photometry, also known as flame emission spectrometry, is a technique used for the qualitative and quantitative analysis of elements present in a sample using a flame as the source of excitation energy. The concept of flame photometry was realized in the early 1860s by Kirchhoff and Bunsen, who discovered that specific elements emit characteristic radiation when excited in flames. The first instrument developed for this purpose was used to measure sodium (Na) in plant ash using a Bunsen...
Atomic Emission Spectroscopy: Lab01:29

Atomic Emission Spectroscopy: Lab

AES is a powerful analytical technique, especially effective when used with plasma sources, producing abundant spectra in characteristic emission lines. The Inductively Coupled Plasma (ICP), in particular, yields superior quantitative analytical data due to its high stability, low noise, low background, and minimal interferences under optimal experimental conditions. However, newer air-operated microwave sources are emerging as promising alternatives that could be more cost-effective than...
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Atomic Absorption Spectroscopy: Interference

Interference leads to systematic error in atomic absorption (AA) measurements by enhancing or diminishing the analytical signal or the background. These interferences can be grouped into three main categories: spectral interference, chemical interference, and physical interference.
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Atomic Emission Spectroscopy: Interference01:30

Atomic Emission Spectroscopy: Interference

In atomic emission spectroscopy (AES), high-temperature atomizers excite a broad range of elements and molecules that generate complex emissions from sources such as oxides, hydroxides, and flame combustion products in the flame or plasma. Several strategies can be employed to minimize spectral interferences caused by overlapping emission lines or bands. These include increasing instrument resolution, choosing alternative emission lines, optimally placing the detector in low-background regions,...

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Related Experiment Video

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Split Point Analysis and Uncertainty Quantification of Thermal-Optical Organic/Elemental Carbon Measurements
10:22

Split Point Analysis and Uncertainty Quantification of Thermal-Optical Organic/Elemental Carbon Measurements

Published on: September 7, 2019

Harmonizing aerosol carbon measurements between two conventional thermal/optical analysis methods.

Guorui Zhi1, Yingjun Chen, Junying Sun

  • 1Chinese Academy of Meteorological Sciences, Beijing 100081, China. zhigr68@yahoo.com.cn

Environmental Science & Technology
|March 4, 2011
PubMed
Summary

This study quantifies the difference between NIOSH and IMPROVE thermal/optical analysis (TOA) protocols for elemental carbon (EC) and organic carbon (OC) measurements. A regression equation harmonizes inconsistent EC/TC ratio data, improving aerosol carbon analysis.

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Area of Science:

  • Environmental Science
  • Analytical Chemistry
  • Atmospheric Science

Background:

  • Total carbon (TC) measurement is consistent, but differentiating organic carbon (OC) and elemental carbon (EC) is inconsistent.
  • The NIOSH and IMPROVE protocols are standard for thermal/optical analysis (TOA), but yield different EC values.
  • Previous studies indicate the NIOSH protocol typically yields lower EC than the IMPROVE protocol.

Purpose of the Study:

  • To quantitatively link the differences observed between the NIOSH and IMPROVE TOA protocols.
  • To develop a method for harmonizing inconsistent EC/TC ratio measurements from different TOA protocols.

Main Methods:

  • Reanalyzed residential coal-burning samples using the IMPROVE protocol after initial analysis with the NIOSH protocol.
  • Compared EC values obtained from both protocols.
  • Developed a regression equation to describe the relationship between the EC/TC ratios from the two protocols.

Main Results:

  • Established a dynamic relationship between the NIOSH and IMPROVE protocols.
  • Derived a regression equation: y=(1-x)/(1+4.86x2) (R2=0.96), where x is the IMPROVE EC/TC ratio and y is the relative difference between IMPROVE and NIOSH EC/TC.
  • Achieved high correlation (R2=0.96) between the derived relationship and the experimental data.

Conclusions:

  • The developed regression equation provides the first quantitative link between the two major TOA protocols.
  • This equation can harmonize inconsistent TOA measurements for applications like source characterization, ambient monitoring, and atmospheric modeling.
  • Improved consistency in EC/TC measurements will enhance the accuracy of aerosol carbon analysis.