Environmental Analysis

Integration of Environmental Analysis


"Scientists' understanding of the environment can only be as good as their knowledge of the identities and quantities of pollutants and other chemical species in water, air, soil, and biological systems. Therefore, proven, state-of-the-art techniques of chemical analysis, properly employed, are essential to environmental chemistry." Manahan, 10th ed. pg. 705
What is your concept of the relationships between the following:

How are environmental issues evaluated ?


"Environmental Chemical Analysis"

(The text chapter 24)

Provides an overview of many methods of analysis. We will concentrate on the ones you will use in your laboratories.

The others are there as a survey or overview. We will discuss them in general but will describe only several in depth.
Overview of methods:

Some Categories of Analysis:
  Analytical Technique Related

  Matrix Specific


Overview of Selected Chemical Analysis Methods

Classical Methods

Use mostly manual equipment and older methods

Examples of classical methods:

Spectroscopic Method
Use light interactions with molecules, complexes, atoms or ions to qualitatively and quantitatively evaluate chemical components of environmental samples

Examples:

Titration example - The titration with an indicator of Ca (and/or Mg) ions in water using EDTA are examples of a classical analysis.
Ca2+ (or Mg2+) + H2Y2- ----> CaY2- (or MgY2- ) + 2H+


Gravimetric example - Precipitation of silver with Chloride ion is an example of a classical gravimetric analysis.
Ag(aq) + Cl(aq) ---> AgCl(s)

Combination of several classical methods produce complex reaction groups of dependent reactions.

DO (dissolved oxygen)
Volumetric example - Oxidation-reduction-titration-volumetric, dissolved oxygen (DO) (Winkler method) being done in constant volume bottles and comparing relative iodine color is an example of volumetric and titrimetric analysis.

Mn+2+ 2OH- 1/2 O2 ---> MnO2(s) + H2O

MnO2(s) + 2I- + 4H+ ---> Mn+2 + I2 + H2O

I + 2S2 O32- ---> S4 O62- + 2I-



Oxygen dissolved in water oxidizes manganese from +2 to +4 in basic solution. The acidification of the hydrated MnO2 in the presence of I- to release free I2, then titrate free I2 with thiosulfate with starch providing the endpoint.

BOD Biochemical Oxygen Demand
Air saturate water samples in a standard size bottle (usually). Then add a biological "seed"and incubate for 5 days. Estimate the amount of biodegradable organic matter in the water to determine the remaining dissolved oxygen. This is usually expressed in mg/l; where mg is of oxygen.

Absorption and emission are two fundamental principles

Beer's Law is one of the most common relationships applied

Beer's Law:   A=abc

Where:
A = Absorbance
a = absorptivity, (wavelength-dependent)
b = is the path length the light travels through the absorbing solution
C = concentration of the absorbing material in solution

This fundamental relationship is the key parameter in:
Molecular absorption
Colorimetric analysis
Atomic absorption

Survey of Analytical Techniques

Review for familiarity in general.
These will produce the data used in environmental evaluation.

Examples:
  Atomic absorption         Traditional Lab. method
  Atomic emission
    Flame
    ICP-OES
  X-ray fluorescence         optical emission Spect.& a new field method, Survey only!

Electrochemical methods
    note: many interferences when using real samples

Mass Spectrometry (MS)
    Organic
    Inorganic Chromatography
    Gas Chromatography (GC)
    Liquid Chromatography (LC)
      also call high performance L.C. or (HPLC)
    Supercritical Fluid Chromatography (SFC)
    Ion Chromatography

Hyphenated Techniques
    GC-MS
    LC-MS
    ICP-MS
    LC-ICP-MS

Sample Preparation

Sample preparation must be done on real environmental samples prior to analysis.

Extraction
Organic------------ organic solvent extraction
Inorganic---------- acid extraction

Dissolution
Organic------------ organic solvent
Inorganic---------- acid decomposition

Purge and Trap
for volatile organic components, such as, in soil (gasoline)

Physical Properties

In water for example:

Turbidity
Temperature
Color
Conductance
Specific Gravity

In soils and sediments:

Particle size
Color
Physical phases
Obvious structure

Chemical Properties specific to the matrix and sample

Tests Specific to the Sample:
BOD (biological oxygen demand) in water
DO (dissolved oxygen) in water
Extraction from matrix in soils, and in sediments
pH in water
Total Alkalinity in water
O3 (ozone) in air
NOx in air (ps)
SO2 in air, (ps), point source

The new trend is field analytical methods

(not in text)

Example:
X-ray fluorescence

Example:
Method 7473 for Hg analysis (RCRA update VI)

Example:
Field portable laboratory trailers take lab to the field.

Specific inorganic instrument used in the laboratory

Microwave Sample Decomposition Standard EPA Procedure
EPA RCRA Methods 3051a, 3015a, 3052, 3050B, (and others)
Inactively Coupled Plasma-Mass Spectrometry (ICP-MS) Standard EPA Procedure
EPA RCRA Methods 36020 (update VI 6020a)

Literature and Readings

National Science Foundation (NSF) Problem Based Learning, PBL discussion: (applies to sampling and laboratory philosophy).

References for Laboratory:
"Curricular Developments in the Analytical Sciences, A Report from the Workships"
National Science Foundation, Washington DC, September 12, 1997, pages 2-6.

Standard EPA Methods:

EPA RCRA Method 3051a (update VI, 1998)
"Microwave Assisted Acid Dissolution of Sediments, Sludges, Soils, Oils"

EPA RCRA Method 6020 (update III, 1996) "Inductively Coupled Plasma - Mass Spectrometry"

EPA RCRA quality assureance chapter 3 (update VI, 1998) "Clean Chemistry and the Analytical Blank"

Mass Spectrometry


Mass spectrometric methods are referred to as particle methods

Overview:

Hyphenated techniques are frequently formed using mass spectrometry coupled with GC and HPLC. MS came later and increased the utility of the methods.
Method includes:
GC-MS
LC-MS (or HPLC-MS ), Organic or Inorganic

Direct introduction of liquid or gas samples for inorganic ICP-MS

The Method - Mass Spectrometry Fundamentals

The method includes and depends on:

1. Production of a gaseous ion and/or ion fragments [Uniform fractionation patterns from specific instrument configurations producing identical patterns]
{Standardized and Comparable Patterns}

2. The measurement of a change to mass ratio in a vacuum [m/z] (collision free path requires at least 10-6 torr)

3. A stable uniform and consistent ionization source to produce reproducible ionization

4. Measurement of relative abundance of ions or fragments of each mass without bias


Fundamental Components of Mass Spectrometry

Sample Introduction System (inlet system)
Ionization System
Vacuum System
Mass Analyzer (Mass Separator)
Ion Collection and (Mass Detection)
Basis of measurement is mass-to-charge ratios
Data Manipulation and Molecular Identification System
(sometimes associated with sophisticated data base, searching and spectral analysis capability)

Methods of Sample Introduction

Configurations and Hyphenation

Frequently the mass spectrometer is interfaced with some sample treatment and separation device.

1.Direct Liquid Introduction   lab will use this method
2. Liquid Chromatography
3. Gas Chromatography
4. Gas, Aerosol, Particle Introduction
5. Laser Ablation
5. Solid Samples
6. Inductively Coupled Plasma


Mass Analyzers

Different Mass Analyzer Types
The two main types of mass analyzers are Sector and Dynamic mass analyzers

Sector Mass Analyzers
Magnetic Sector Analyzers
    Single focusing
    Double focusing
    Triple focusing
Electrostatic Sector Analyzers

Dynamic Mass Analyzers
Quadrupole   Both Lab ICP-MS's use this one
Cyclotron Resonance Mass Analyzer
Ion Trap
Time of Flight

Ion Detection

Three main types:
1. Electron Multiplier   Both Lab ICP-MS's use these
2. Faraday Cup Collector   Both Lab ICP-MS's use these
3. Channel Electron Multiplier Array

Faraday Cup Collector Detection

An electrically connected cage into which the ions are directed

Electrons are supplied through a circuit and the potential change in the cage is amplified to obtain a signal.

The Faraday Cup detector is very stable but it has no internal amplification ( a one for one - one ion produces one electron). (see figure below)

Electron Multiplier Detection

This type is the most important and most common.

Two discrete types:
Continuous dynode electron multiplier (most popular)
Discrete dynode electron multiplier

In discrete dynode multiplier each dynode is held at successively higher voltages amplifying the signal.

Up to 20 dynodes are available with a current gain of 107 - 108 electrons per ion

Continuous dynode is glass doped with Pb with a potential of 1.8-2kV across the length of a trumpet shaped detector. Ions striking the surface near the entrance eject electrons that skip along the surface ejecting electrons. Current gains of 105 to 108 are possible.

Figures S&L pg. 426-427 Figures 18-3 - 18-4.

1. Faraday Cup detector

2. Discrete dynode electron multiplier and

3. Continuous dynode electron multiplier (most popular)

These detectors require vacuum to prevent arcing and to preserve their electrical coatings.


Data Acquisition


Scanning the Mass Range

Data can be obtained in several ways depending on the objective.

Scanning is one way to produce peaks of the different mass ions (or more correctly the charge to mass ratios m/z).

Peak Hopping

The mass analyzer can be set to look for the mass of interest based on an elemental ion or a molecular form expected in the sample.

Analysis of the intensity of the mass signal compared against some standard is the usual way of quantifying the unknown concentration.

Inductively Coupled Plasma (ICP) as the Ion Source

A very important ion source that you should be able to explain.

Inductively Coupled Plasma is an important Ion Source and is mainly useful in inorganic mass spectrometry as the temperature is too high to be of use in organic mass spectrometry.

It is based on a Torch and Plasma generator

The Inductively Coupled Plasma (ICP) torch is an electrodeless discharge in a gas at essentially atmospheric pressure maintained by energy coupled to it from a radio frequency generator.

The energy is coupled by a coil functioning as a primary radio frequency transformer and the secondary is created by the discharge itself.

The plasma is generated at the open end of the torch which is a quartz tube assemble of 2 inner tubes, one to transport the sample and carrier gas, and an outer tube to transport the gas volume necessary to supply the plasma with gas to ionize.

Typical Plasma Torch Configuration:
The torch usually consists of 3 concentric tubes.
1. inner,
2. middle, and
3. outer.

Typical dimensions are in 1.5 mm inner diameter tube (supplying the sample); contained inside a 13 mm middle tube supplying the gas to make up the bulk of the plasma usually 10 times the flow of the sample stream but is usually supplied in a spiral direction to help form the plasma. Both the inner and middle tubes terminate within a centimeter of the end of the torch. The outer quartz tube is usually 10 mm and contains the other two tubes. The radio frequency (RF) generator coils are located around the outer tube.


ICP Plasma Potential and Secondary Discharge

Carrier and plasma gases are usually Argon, the torch is usually quartz and the RF (radio frequency, actually it is a microwave frequency) coil is water cooled copper to prevent it from melting.

The RF energy is 27 or 40 Mhz coupled to it by the load coil.

The generator is usually operated at a 1-1.5 kW supplyng the RF to the induction coils.

Power requirements to maintain the induced plasma are between 0.75 and 2.0 kW.

The Argon plasma is maintained at 5,000 to 9,000 °C.

Inductively Coupled Plasma as the Ion Source


Figure 2.1 JGH (shows a typical plasma torch assembly and induction coil design.




The torch is mounted with its axis horizontally for extraction of the ions into the mass spectrometer.



The Inductively Coupled Plasma Ion Source Requires a Unique Instrument Interface.

The ICP-MS usually requires samples to be introduced into a flowing stream of argon (sometimes He and other inert gases are used) such as:
Gas
Vapor
Aerosol
Solid Particles (very fine size)

Figure 2.8 Demonstrates the entire assembly for Torch, two Cones (Sampling and Skimmer), and the accelerations of the positive ions by a negative voltage field behind the second cone.

Torch   Instrument interface with two extraction cones



Ion Extraction

The gas is drawn into the region between the two cones by a vacum and reaches supersonic velocities as it expands in the vacuum chamber and reaches the skimmer orifice in a few micro seconds (µs).

Figure 2.12 JGH illustrates the sampler and skimmer with the ions in between where they are propelled at supersonic speeds and how light and heavy ions are accelerated at the same velocity (v) as neutral Ar in the jet. Figure 2.13 not reproduced there also helps illustrate this effect.



This supersonic jet is demonstrated graphically in Figure 2.12 where it also demonstrates the reason for the kinetic energy enhancement of the heavier ions. Since all the ions are traveling at the same speed the heavier ions with a larger mass (m) have more kinetic energy as demonstrated previously in Figure 2.14.

After Ionization, Ions are Collected Accelerated

The positive ions are accelerated by charged plates in a vacuum.

Only negative acceleration plates are customarily used.

where:
The kinetic energy (KE) that is added to the ion is due to the acceleration potential V and is given by:

The KE of mass m and charge z is expressed as:

KE = eV = zeV = 1/2mv2

where: v is the velocity after the ion is accelerated and e is the charge of the ion (e = 1.60 x 10-19 C {coulombs})

Thus trajectories are based on the laws of physics used in the design of the Mass Analyzers or mass separators used to discriminate m/z ions Figure 18-19 S&L (Skoog and Lerie)

Lense collection and acceleration


Quadrupole Mass Analyzer

A field is formed by four electrically conducting, parallel rods.

The rods work as opposite pairs.

The mass analyzer is in a section of the mass spectrometer with progressively lower vacuum of between 10-7 - 10-8 Pa or 10-5 - 10-6 torr.

The quadrupole mass analyzer can operate in relatively low vacuum such as 10-4 torr but there must be enough vacuum to prevent arching from the quadrupoles.

The ions enter on a linear flight path in the z direction and are directed by means of the electric fields in the x and y direction. Unwanted ions of non selected m/z ratio oscillate with increasing amplitude and collide with the quadrupoles acting as electrodes and become neutral particles.

Selected ions proceed through the quadrupole mass analyzer and are detected.

By controlling the potential on the quadrupole, only one m/z ion will be permitted at a time to emerge and proceed to the detector.

m/z ratio - is mass/charge ratio

Quadrupole mass analyzers are solid state devices and do not have any moving parts.

The only moving parts are in the vacuum system.

Figure 20.6 (SH) demonstrates how the quadrupole blocks all ion mass to charge ratios except the one being analyzed, which is sent on to the detector.




How the Quadrupole Functions

The quadrupole functions as two sets of mass filters similar to optical cut-off filters. Sets of filters called Set (a) and Set (q).

Each set has different cut-offs for high m/z or low m/z.

Figures 2.20 and 2.21 (JGH) demonstrate the function of the quadrupole.






Instrument Sample Introduction Options


This section discusses options for sample introduction including:
Nebulizers
Spray Chambers
Plasma Torches, and
Sampling Cones

Note: The great majority of analysis done on ICP-MS instruments are done on liquid samples.

A gas stream is required for introduction into the ICP-MS, and thus a liquid stream must be converted.

An aerosol is the most convenient form of liquid sample at present.

Related rational for the laboratories structured.

Other experts who suggest using the approach that we are taking in these laboratories (modeling, sampling, and analysis) have studied your needs as future professionals and how to help you gain these skills.



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Revised 4/15/99.