91 |
Heavy metal tolerance, uptake and accumulation in populations of Typha latifolia L. and Phragmites australis (Cav.) trin ex. streudelYe, Zhi Hong January 1995 (has links)
No description available.
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92 |
Gravel bed hydroponic treatment of metal contaminated wastewaterBrown, Andrew Charles January 1996 (has links)
No description available.
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93 |
The interactions of toluic acid with indigenous microbial populations in a model Gravel Bed Hydroponic systemFuller, Robert A. January 1996 (has links)
No description available.
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94 |
An investigation of the microbial ecology of biofilms from a model gravel bed hydroponic systemWebster, Alison Mary January 1999 (has links)
No description available.
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95 |
Influence of plant operating conditions on the dewaterability of surplus activated sludgeJiwani, Ashifa January 1996 (has links)
No description available.
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96 |
The use of biosorption, elution and electrolysis for the removal and recovery of heavy metals from aqueous solutionsButter, Timothy John January 1998 (has links)
No description available.
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97 |
The application of jet loop reactors for industrial wastewater treatmentBloor, J. C. January 1995 (has links)
No description available.
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98 |
Predicting algal concentration in waste stabilisation pondsWeatherell, Charlotte Anna January 2001 (has links)
No description available.
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99 |
The electrochemistry of silver co-ordination complexesBolger, Paul Thomas January 1999 (has links)
No description available.
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100 |
Investigation of Biologically-produced Solids in Moving Bed Bioreactor (MBBR) Treatment SystemsSoleimani Karizmeh, Mohsen 07 November 2012 (has links)
Lower production rate of solids in attached growth moving bed bioreactor (MBBR) systems as compared to conventional activated sludge (AS) systems makes them an attractive choice for municipal wastewater treatment (Ødergaard et al. 1994). However, the production of biologically-produced solids in MBBR systems is currently not well defined and requires additional investigation.
Three identical MBBR reactors were operated under the same dissolved oxygen (DO) concentration, influent pH and volume of Anoxkalnes media in two different experimental phases. In the first phase, the hydraulic retention time (HRT) kept constant in three reactors and SALR increased and in the second phase, the SALR was the constant parameter while HRT increased. These two phases were implemented to investigate the effect of variations in HRT and SALR on biologically-produced solids in MBBR reactors. This study demonstrated that HRT and SALR play an important role in settling characteristics of the biologically-produced solids in MBBR systems.
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