Introduction to Advanced Oxidation Processes (AOPs) and
Photochemical Based AOPs
James Bolton (U of A, Edmonton, Canada) and
Thomas Oppenländer
Hochschule Furtwangen University, Germany Department of Process Engineering
Outline
Definitions
Survey: Advanced Oxidation Technologies The Hydroxyl Radical
AOT Mechanism
Basics of Photochemistry UV Treatment of NDMA
Development Status of Photochemical AOTs Organic Parameters of Water Analysis
Some important definitions
AOP: Advanced Oxidation Process AOT: Advanced Oxidation Technology UV: ultraviolet radiation
VUV: vacuum-UV radiation between 100
nm and 200 nm
Advanced Oxidation Technologies (AOTs)
Usually involve the generation of hydroxyl radicals (•OH).
Called “Advanced” because the reactions are just highly accelerated oxidation reactions that occur when pollutants enter the environment.
The •OH radicals react with organic pollutants to initiate a series of oxidative degradation reactions.
The overall process often leads to mineralization (i.e., conversion to CO2, H2O and mineral acids) of the pollutants.
Photochemical Processes
Advanced Oxidation Processes and
Technologies:
AOPs AOTs Solar Processes TiO Photocatalysis2
Super Critical Water Oxidation
(SUWOX) Catalytic
Processes
Sonolysis Non-thermal
Plasma Techniques
γ-Radiolysis Electron Beam
Irradiation
X-Ray Irradiation Electrochemical
Processes
Survey of Advanced Oxidation Processes (AOPs)
Short Lived
Highly Reactive Powerful
Oxidant
Ubiquitous in Nature
Easy to Produce
Non-Selective Reagent
O H
• _ _
Electrophilic Character Kinetic Reaction
Control
The Hydroxyl Radical
The Hydroxyl Radical
Reacts (usually with very high rate constants) by hydrogen abstraction (saturated aliphatics) addition to double bonds (unsaturated &
aromatics)
electron transfer (primarily with inorganics) radical-radical reactions (e.g., ••••OH + HO2••••) Molar absorption coefficients
εεεε230= 530 M-1cm-1; εεεε260= 370 M-1cm-1 pKa= 11.9
Eo= 2.7 V (acid solution)
AOT mechanism
••••OH + CH3OH ••••CH2OH + H2O
• •OH radicals react with organic compounds by:
• hydrogen abstraction from aliphatic compounds
addition to unsaturated compounds
••••OH + CH2= CH2 ••••CH2CH2OH
• This is followed by reaction with oxygen initiating a series of degradative oxidation reactions
Mechanism of methanol degradation
Other organics are more complex, but generally:
pollutant aldehydes carboxylic acids bicarbonate
••••OH + CH3OH ••••CH2OH
O2 O
HCH + HO2••••
••••OH/O2
O CO2 HCOH
AOT mechanism: oxidation and mineralization
Photo- initiated
AOP
•OH
Mi H O2
Mi•
•O •2 M -O-Oi •
Hydrogen Abstraction Electrophilic Addition
II II
M -O-Oi II •II ?
Mi ox
M2 ox
M1 ox
HO2•/O• H O /O
2
2 2 2
-
HCO3
- HO-
HCO3•/CO •3 -
Mi
Peroxyl Radicals
M3 ox
Electron Transfer
Selective Oxidation
CO2
Tasks of AOTs for water and air treatment
Oxidation of undesirable organic water contaminants R-H R-Hox
Mineralization of organic water contents R-CH2-X CO2 + H2O + HX + ……
Detoxification and purification of Water and air
Basics of Photochemistry (1)
Photochemistry
Photophysics Photobiology
Photo- medicine
Absorption
Fluorescence Phosphorescence
Excited State Properties
Energy or Electron Transfer
Deactivation Mechanisms Formation of
Photoproducts Photochemical
Engineering
Basics of Photochemistry (2)
Reaction System
Lamp Technology
Chemical Engineering
Photochemical Engineering Chemical Analysis
UV/VIS-Spectroscopy and Actinometry
Photoreactor Concepts
Basics of Photochemistry (3)
0 200 400 600 800 1000 1200
0 200 400 600 800 1000 Wavelengthλ/ nm
RadiantEnergyQλof NAPhotons/kJmol-1
E = p N hcA 0/λ
Basics of Photochemistry (4)
0 10 20 30 40 50 60 70
0 200 400 600 800 1000 1200 Wavelengthλ /nm
Near IR IR VIS = Light UV-A UV-B UV-C VUV X-ray γ-ray M M + e+ - Photoionization
Photoexcitation
M Mvib Vibrational Excitation M M*
Basics of Photochemistry (5)
Incident Beam Reflection
Refraction Absorption
Formation of Photoproducts Transmitted Beam Scattering Transparent
Material
Luminescence
Basics of Photochemistry (6) Rate of a Photochemical Reaction
V RC====GFCΦΦΦΦC
G= incident photon flow (einstein s-1) FC = f(λλλλ)χχχχC= fraction of light absorbed by
component C Φ
Φ Φ
ΦC= quantum yield of component C V= volume (L)
Rate (RC) of photochemical reaction of component C
Basics of Photochemistry (7): Definitions
Total fraction of light absorbed
Fraction absorbed by a single component i
Quantum Yield (ΦΦΦΦp)- defined as the number of moles of product formed or reactant removed (P) per mole of photons absorbed.
) 10 ( 1 )
(λλλλ Aλλλλ f ==== −−−− −−−−
a ci i εεεεi
χχχχ ====
absorbed )
(einsteins photons
of moles
generated of
moles
p
==== P ΦΦ ΦΦ
Basics of Photochemistry (8):
Kinetic Regimes
If FCis near unity, the kinetics will be “zero-order”, that is RCwill be independent of cC.
If FCis < 0.1, f(λλλλ) may be expanded in a Taylor Series so that RCreduces to:
such that now the kinetics are “first-order”, that is,RCis proportional to cC.
l V c
RC≈≈≈≈GΦΦΦΦCln(10)εεεεC C
Treatment of NDMA
NDMA (N-nitrosodimethylamine) is a carcinogen that is often found in industrial effluents. It does not biodegrade, air strip or adsorb well to activated carbon. However, it does photolyze very efficiently.
NDMA absorbs only in the range 200–250 nm;
thus, a UV lamp with strong output in this region is essential for effective treatment.
(CH3)2NNO h
νννν
(CH3)2N• + NOUV Treatment of NDMA: Degradation Curves at Different Concentrations
0.0001 0.001 0.01 0.1 1
0 2 4 6 8 10 12 14
time / min
concentration / mM
0.0 0.2 0.4 0.6 0.8 1.0
concentration / mM
k1= 1.31 min-1 k0= 0.164 mM min-1
Question: Which degradation curve represents zero and which first order degradation kinetics?
VUV Oxidation UV Oxidation Photocatalysis UV Disinfection
H O-VUV2 H O -UV O -UV O -H O -UV
2 2
3
3 2 2
TiO -UV/VIS H O -Fe /Fe -
UV/VIS (Photo- )
2
2 2
2+ 3+
Fenton
UV-C
Xe * Excimer Lamp(172 nm)
2 MP
Mercury Lamps
UV-A Lamps Solar UV/VIS
LP and MP Mercury Lamps
Research Industry Industry
Suprasil LP Hg Lamps (185 nm)
Hetero- geneous
Homo- geneous
Homogeneous Homogeneous Homogeneous
Development status of photochemical AOTs
VUV Oxidation UV Oxidation Photocatalysis UV Disinfection
H O-VUV2 H O -UV O -UV O -H O -UV
2 2
3
3 2 2
TiO -UV/VIS H O -Fe /Fe -
UV/VIS (Photo- )
2
2 2
2+ 3+
Fenton
UV-C
Xe * Excimer Lamp(172 nm)
2 MP
Mercury Lamps
UV-A Lamps Solar UV/VIS
LP and MP Mercury Lamps
Research Industry Industry
Suprasil LP Hg Lamps (185 nm)
Hetero- geneous
Homo- geneous
Homogeneous Homogeneous Homogeneous
Development status of photochemical AOTs
Organic Parameters of Water Analysis (1): Global Parameters
T C : T o t a l C a r b o n T I C : T o t a l I n o r g a n i c C a r b o n T O C : T o t a l O r g a n i c C a r b o n D O C : D i s s o l v e d O r g a n i c C a r b o n P O C : P a r t i c u l a t e O r g a n i c C a r b o n V O C : V o l a t i l e O r g a n i c C a r b o n
Organic Parameters of Water Analysis (2):
Group Parameters and Lead Substances
TOX: Total Organic Halogen
DOX: Dissolved Organic Halogen AOX: Adsorbable Organic Halogen EOX: Extractable Organic Halogen POX: Purgable Organic Halogen
VOX: Volatile Organic Halogen
Lead Substrates NOM: Natural Organic Matter HC: Hydrocarbons
PAH: Polycyclic Aromatic HCs
Phenols
Chlorophenols
etc.
Hyperlinks >>>>
Measurement of TOC with a TOC analyzer with auto sampling unit
Combustion of the probe at a catalyst surface and quantification of CO2
Second Order Rate Constants of OH-Radical Reactions with different Substrates:
Typical elementary reaction Substrate + ・OH Product
Rate
(-substrate)= - k
・OH, M[ ・ OH] [Substrate]
Examples of Second Order Rate Constants of OH- Radical Reactions with different Substrates:
rate = - k
・・・・OH, M[
・・・・OH] [Substrate]
Free Database:
http://kinetics.nist.gov/solution/
… for example:
… results:
Rationalization
O O O
H H H
O O
H O H H
HO2• + CH2O Hydroperoxyl Radicals
and Formaldehyde
Medium Pressure Hg Lamp: Emission Spectrum
0,0 0,5 1,0 1,5 2,0
200 400 600 800 1000
Wavelengthλ/ nm SpectralIrradiance Eλ/Wm-2 nm-1
MP Mercury Lamp QC 1000 Enhanced
Emission (UV-C)
Low Pressure Hg Lamp: Emission Spectrum
0,0 0,2 0,4 0,6 0,8 1,0
200 400 600 800 1000 1200 LP Mercury Lamp
NNI 120/84 λ = 253.7 nm
0,0 0,2 0,4 0,6 0,8 1,0
200 400 600 800 1000 1200 λ = 253.7 nmLP Mercury Lamp
NN 50/81
Wavelength / nmλ Spectral Irradiance E, Relative Unitsλ