Dyestuffs are widely used industrial chemicals, yet surprisingly little is known about their
fate in the environment. The potential modes of transformation and removal of reactive
dyes in treatment and in the environment are principally through anaerobic and aerobic
biodegradation and photodegradation. The research herein describes the use of LC-MS
analysis with laboratory simulations to develop a better understanding of the occurrence
and fate of reactive dyes and their degradation products in the aquatic environment.
One reason for the lack of information on the environmental fate of reactive dyes has been
the paucity of robust analytical methods suitable for the determination of dyes in aqueous
samples. Robust analytical methods were optimised to provide LC-MS and MSMS
identification of degradation products. Additionally, interpretation of the MSMS spectra
of known reactive dyes provided novel characteristic fragment ions indicative of the
triazine reactive group of reactive dyes
.
Fibre reactive dyes are designed to have a degree of photostability and therefore their
photodegradation behaviour has not been widely investigated. Little is known of their
stability to daylight over prolonged periods of irradiation in dilute aqueous solutions and in
the presence of humic substances. The kinetics of photodegradation of an anthraquinone
dye (Reactive Blue H4R) and azo dye (Reactive Yellow P5G) were evaluated. The former
underwent rapid and extensive degradation 01/2 1.5 h). The major products formed were
identified using LC-MSMS and a photodegradation pathway proposed. By comparison,
the photodegradation of the azo dye was significantly slower, 01/2 30 h). The addition of
humic substancesa ppearedt o have little effect on the rate of photodegradationu nder the
conditions used.
The reduction of azo dyes under anaerobic treatment has been extensively studied, but the
subsequent fate of the initial reduction products when exposed to air are not understood.
Three relatively simple azo dyes, Amaranth, Sunset Yellow and Naphthol Blue-Black,
were reduced and their autoxidation products identified by LC-MS. These were
subsequently used to predict the autoxidation products of a more complex azo reactive
dye: Reactive Red 3.1. Additionally, a persistent degradation product from the anaerobicaerobic
treatment of Reactive Red 3.1 was identified from LC-MS data.
Azo reactive dyes are generally regarded as being resistant to aerobic degradation and there
are few published data regarding degradation pathways for reactive anthraquinone dyes.
Pure cultures of Pseudomonas docunhae, A 9046 and A texaco and mixed bacterial
consortia (semi-continuous activated sludge, SCAS) aerobic degradation of azo and
anthraquinone reactive dyes was studied. Two azo dyes were degraded by pure cultures of
A docunhae and A 9046, suggesting that azo dyes can be aerobically degraded given
favourable conditions. The antraquinone dye was extensively degraded by SCAS and pure
culture biodegradation. Metabolites were identified by LC-MS and a degradation pathway
proposed.
Date of Award | 2001 |
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Original language | English |
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Awarding Institution | |
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- Aquatic Environment
- Chemistry of
- Organic Water Pollution
- Water Pollution
- Sewage
- Biomedical Engineering
- Biochemical Engineering
An evaluation of the environmental fate of reactive dyes
Hetheridge, M. J. (Author). 2001
Student thesis: PhD