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Vermiculture in Egypt: - FAO - Regional Office for the Near East and

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properties of <strong>the</strong> treated sludge, <strong>the</strong> microbial community <strong>in</strong> <strong>the</strong> biofilm, <strong>and</strong> <strong>the</strong><br />

earthworm–microorganism <strong>in</strong>teractions <strong>in</strong> <strong>the</strong> vermifilter reactor. The results of this<br />

study provide useful <strong>in</strong><strong>for</strong>mation regard<strong>in</strong>g <strong>the</strong> use of a vermifilter <strong>for</strong> <strong>the</strong> optimal<br />

sewage sludge treatment. A cyl<strong>in</strong>der shaped vermifilter (30 cm <strong>in</strong> diameter <strong>and</strong> 60 cm<br />

<strong>in</strong> depth) that was naturally ventilated was equipped with a 0.5-<strong>in</strong>ch polypropylene<br />

pipe with holes to ensure uni<strong>for</strong>m distribution of <strong>the</strong> <strong>in</strong>fluent (Figure 7.3). The<br />

vermifilter conta<strong>in</strong>ed a 0.5 m filter bed of ceramic pellets (6–9 mm <strong>in</strong> diameter). A<br />

layer of plastic fiber was placed on <strong>the</strong> top of <strong>the</strong> filter bed to avoid direct hydraulic<br />

impact on <strong>the</strong> earthworms <strong>and</strong> to ensure an even <strong>in</strong>fluent distribution. The <strong>in</strong>fluent<br />

sludge was <strong>in</strong>troduced to <strong>the</strong> vermifilter via a peristaltic pump. After pass<strong>in</strong>g through<br />

<strong>the</strong> filter bed, <strong>the</strong> treated sludge entered <strong>in</strong>to a sedimentation tank below <strong>the</strong><br />

vermifilter <strong>and</strong> <strong>the</strong> supernatant <strong>in</strong> <strong>the</strong> sedimentation tank was recycled.<br />

Figure 7.3. Layout of <strong>the</strong> Vermifilter<br />

Source: Zhaoa et al. (2010).<br />

The vermifilter may be an efficient technology <strong>for</strong> stabilization of excess sludge from<br />

domestic Waste Water Treatment Plants. The volatile suspended solids (VSS)<br />

reduction <strong>in</strong> <strong>the</strong> VF reached 56.2–66.6%, which met <strong>the</strong> criteria <strong>for</strong> aerobic <strong>and</strong><br />

anaerobic sludge stabilization (>40%). The presence of <strong>the</strong> earthworms <strong>in</strong> <strong>the</strong> VF<br />

<strong>in</strong>duced an additional 25.1% reduction <strong>in</strong> volatile suspended solids. On average, <strong>the</strong><br />

earthworm–microorganism <strong>in</strong>teractions were responsible <strong>for</strong> approximately 46% of<br />

<strong>the</strong> improvement <strong>in</strong> <strong>the</strong> VSS reduction. Moreover, a detailed characterization of<br />

sludge <strong>and</strong> earthworm cast samples revealed that earthworms <strong>in</strong> <strong>the</strong> VF improved <strong>the</strong><br />

microbial activity by trans<strong>for</strong>m<strong>in</strong>g <strong>in</strong>soluble organic materials <strong>in</strong>to a soluble <strong>for</strong>m <strong>and</strong><br />

selectively digest<strong>in</strong>g <strong>the</strong> sludge particles of 10–200 μm to f<strong>in</strong>er particles of 0–2 μm,<br />

while enhanc<strong>in</strong>g <strong>the</strong> bacterial diversity <strong>in</strong> <strong>the</strong> biofilm. Additionally, improved sludge<br />

settleability with a compact structure <strong>and</strong> low SVI values (33–45 mL/g) were<br />

achieved <strong>in</strong> <strong>the</strong> presence of earthworms, which was favorable <strong>for</strong> fur<strong>the</strong>r sludge<br />

process<strong>in</strong>g (Zhaoa et al., 2010).<br />

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