<?xml version="1.0" encoding="UTF-8"?><?xml-stylesheet type="text/xsl" href="static/style.xsl"?><OAI-PMH xmlns="http://www.openarchives.org/OAI/2.0/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/ http://www.openarchives.org/OAI/2.0/OAI-PMH.xsd"><responseDate>2026-09-19T14:31:46Z</responseDate><request verb="GetRecord" identifier="oai:openscholar.dut.ac.za:10321/485" metadataPrefix="oai_dc">https://openscholar.dut.ac.za/server/oai/request</request><GetRecord><record><header><identifier>oai:openscholar.dut.ac.za:10321/485</identifier><datestamp>2025-03-07T22:45:24Z</datestamp><setSpec>com_10321_9</setSpec><setSpec>col_10321_10</setSpec></header><metadata><oai_dc:dc xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xmlns:doc="http://www.lyncode.com/xoai" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
   <dc:title>Process development for co-digestion of toxic effluents : development of screening procedures</dc:title>
   <dc:creator>Dlamini, Sithembile</dc:creator>
   <dc:contributor>Pillay, Visvanathan Lingamurti</dc:contributor>
   <dc:subject>Sewage</dc:subject>
   <dc:subject>Sewage sludge digestion</dc:subject>
   <dc:subject>Factory and trade waste--Purification</dc:subject>
   <dc:subject>Sewage--Purification--Anaerobic treatment</dc:subject>
   <dc:description>Submitted in partial fulfilment of academic requirements for the degree of Masters of Technology: Chemical Engineering, Durban University of Technology, Durban, South Africa, 2009.</dc:description>
   <dc:description>The primary objective of this project was to establish a screening protocol which could be used&#xd;
to access high strength/toxic effluent for toxicity and degradability prior to being disposed in&#xd;
wastewater treatment works.&#xd;
The serum bottle method (materials and method section) is simple, makes use of small glass vials&#xd;
(125 mℓ-volume were used in this research) which do not require any stirring nor feeding device&#xd;
or other engineered tool: a serum bottle is sealed immediately after all components are poured&#xd;
inside and thereafter conducted in a batch mode and occasionally shaken to ensure adequate&#xd;
homogenisation of the components. The only variables which are regularly measured are the&#xd;
volume of biogas produced and gas composition. The two assays, originally developed by&#xd;
Owen et al. (1979) to address the toxicity and the biodegradability have been combined in a&#xd;
single test called AAT, Anaerobic Activity Test, which enables one to assess simultaneously the&#xd;
inhibitory effect on the methanogenic biomass and the biodegradability of the test material as&#xd;
well as the ability of the biomass to adapt to the test material and therefore to overcome the&#xd;
initial inhibition.&#xd;
The screening protocol is illustrated in Annexure A. The protocol consists of a sequence of&#xd;
assays which employ the serum bottle methodology. A first step of the procedure is aimed at&#xd;
rapidly estimating whether the effluent is potentially toxic to the methanogenic biomass and in&#xd;
what concentration. The second step is a more extensive screening, aimed at precisely&#xd;
characterising the toxicity of the effluent, the extent of biodegradation that can be achieved, as&#xd;
well as at establishing whether a potential for adaptation of the biomass exists upon exposure. If&#xd;
the sample passes the screening stage, the same serum bottle method will be used to conduct a&#xd;
series of batch co-digestion experiments aimed at evaluating a convenient volumetric ratio&#xd;
between the test material and the readily biodegradable substrate. Finally, a laboratory-scale codigestion&#xd;
trial could simulate the full-scale process, thus enabling the selection of appropriate&#xd;
operating conditions for the start-up of the full-scale implementation.&#xd;
This the protocol has been used to assess the amenability to be anaerobically (co)digested of four&#xd;
industrial effluents, i.e. size and distillery effluents which are classified as high strength and&#xd;
scour and synthetic dye effluents classified as toxic. From the biodegradability and toxicity&#xd;
assays the following conclusions were drawn. The size and distillery effluent were found to be&#xd;
ii&#xd;
degradable at 32 g COD/ℓ and 16 g COD /ℓ concentrations respectively. Concentrations higher&#xd;
than these stipulated above were found inhibitory. Scour effluent was found to be recalcitrant at&#xd;
all concentration tested and synthetic dye was 100 % degradable at 0.12 g COD/ℓ and lower and&#xd;
highly inhibitory at concentration higher than 1.1 g COD/ℓ.&#xd;
Co-digestion experiment using serum bottle AAT method were undertaken between effluents i.e.&#xd;
size + distillery, size + scour, distillery + synthetic dye in an attempt to verify whether the&#xd;
digestion performance benefits from simultaneous presence of the two substrates. The volumetric&#xd;
ratios between the effluents were 1:1, 1:2, 2:1. The presence of two mixtures in the case of size&#xd;
and distillery had better methane production compared to individual substrate i.e. size or&#xd;
distillery separate. The mixture with volumetric flow rate ratio of 2:1 (size: distillery) was&#xd;
preferable in terms of process performance as it had highest COD removal compared to the other&#xd;
mixtures /ratios and individual substrates. The mixture of size and scour (2:1) had highest&#xd;
degradation percentage compared to other ratios but not high enough to qualify as degradable&#xd;
(less than 50 %). The mixture of distillery and synthetic dye had the same pattern with ratio of&#xd;
2:1 giving the best COD conversion. The pattern than can be drawn from the degradability of&#xd;
mixtures is: the degradability of mixtures increase with the increasing amount of the most&#xd;
biodegradable compound/effluent in the mixture.&#xd;
Serum bottle results provided the detailed information regarding the safe operating parameters&#xd;
which should be used during the starting point for the larger scale investigation i.e. lab-scale&#xd;
investigations. The lab scale investigations were conducted primarily to validate screening and&#xd;
monitor how the digestion progresses and also to provide data for future project i.e. pilot plant&#xd;
investigation. Other effluents i.e. scour and synthetic dye and their co-digestion mixture were&#xd;
excluded from the lab-scale investigations since they were found to be non- biodegradable i.e.&#xd;
their COD conversion was less the 50 % in the screening protocol. Due to time constrains and&#xd;
other technical difficulties in the laboratory, the co-digestion of size and distillery mixture trials&#xd;
we not conducted on the laboratory scale.&#xd;
Laboratory-scale digestion trials showed that the best organic loading rate for distillery effluent&#xd;
in terms of reactor performance and stability was 1.0g COD/ℓ with efficiency of about 45 %, and&#xd;
for size was 2.0g COD/ℓ with an efficiency of 40 %. The efficiencies obtained in both effluents&#xd;
trials could be greatly improved by acclimation; however these results showed that the digestion&#xd;
of these effluents on the bigger scale is possible.</dc:description>
   <dc:description>Water Research Commission</dc:description>
   <dc:description>M</dc:description>
   <dc:date>2009-11-06T11:37:42Z</dc:date>
   <dc:date>2011-03-31T22:20:06Z</dc:date>
   <dc:date>2009</dc:date>
   <dc:type>Thesis</dc:type>
   <dc:identifier>325132</dc:identifier>
   <dc:identifier>http://hdl.handle.net/10321/485</dc:identifier>
   <dc:identifier>https://doi.org/10.51415/10321/485</dc:identifier>
   <dc:language>en</dc:language>
   <dc:format>191 p</dc:format>
   <dc:format>application/pdf</dc:format>
</oai_dc:dc></metadata></record></GetRecord></OAI-PMH>