APPLICATION OF EXCIMER INCOHERENT-UV SOURCES AS A NEW TOOL IN PHOTOCHEMISTRY - PHOTODEGRADATION OF CHLORINATED DIBENZODIOXINS IN SOLUTION AND ADSORBED ON AQUEOUS PULP SLUDGE
Rs. Nohr et al., APPLICATION OF EXCIMER INCOHERENT-UV SOURCES AS A NEW TOOL IN PHOTOCHEMISTRY - PHOTODEGRADATION OF CHLORINATED DIBENZODIOXINS IN SOLUTION AND ADSORBED ON AQUEOUS PULP SLUDGE, Journal of photochemistry and photobiology. A, Chemistry, 79(1-2), 1994, pp. 141-149
The photolysis at 222 and 308 nm of 2-chlorodibenzo-p-dioxin and 1,2,4
-trichlorodibenzo-p-dioxin dissolved in acetonitrile-water and methano
l-water solutions was studied, using excimer incoherent-UV lamps (KrCl
excimer, 222 nm; XeCl excimer, 308 nm) and an Hg-Xe lamp (wavelength
of 308 nm was selected with a monochromator). Numerous products are fo
rmed: dibenzodioxin, hydroxydibenzodioxin, trihydroxybiphenyl (two iso
mers), dihydroxychlorobiphenyl (two isomers) and trihydroxychlorobiphe
nyl (two isomers) were detected by gas chromatography-mass spectrometr
y (GC-MS) and high performance liquid chromatography (HPLC), and chlor
ide ion by high performance ion chromatography (HPIC). 2,2'-Dihydroxyb
iphenyl is formed as a secondary product. The relative yields of the p
roducts depend on the nature of the organic cosolvent and on whether o
r not the solutions are oxygenated. Quantum yields of substrate destru
ction and of dibenzodioxin and chloride ion formation were determined.
For example, at 308 nm, in deoxygenated and oxygenated acetonitrile-w
ater (50:50, v/v) solution with a solute concentration of 7.5 x 10(-4)
mol dm-3, PHI(2-chlorodibenzodioxin destruction) was 0.08 and 0.10, P
HI(dibenzodioxin) was 0.014 and 0.004 and PHI(Cl-) was 0.04 and 0.05 r
espectively. In methanol-water (50:50, v/v), PHI(dibenzodioxin) is abo
ut 30% higher and is not decreased in the presence of oxygen. The depe
ndence of the nature of the products and the dependence of their relat
ive importance on the nature of the solution indicates that several di
fferent primary processes play a part: (i) homolytic scission of the C
-Cl bond; (ii) heterolytic scission of the C-Cl bond; (iii) homolytic
cleavage of a C-O bond. The latter reaction may lead to reactive quino
ne-type compounds. Photodegradation experiments involving pulp sludge
were performed with 1,2,4-trichlorodibenzodioxin. Higher fluences are
required to produce equal effects when the compound is adsorbed on pul
p sludge rather than homogeneously dissolved, but the destruction of t
he dioxin follows the same (first-order) rate law.