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Heavy Metal Distribution in Anaerobically Digested Sludges MICHAEL S. GOULD, Graduate Assistant EMIL J. GENETELLI, Professor Department of Environmental Sciences Rutgers University New Brunswick, New Jersey 08903 INTRODUCTION Heavy metals in sludges emanating from biological wastewater treatment systems have become a topic of intense interest due to their potential as toxic agents in the environment. These sludges, after anaerobic digestion, are commonly disposed of in landfills, incinerators, oceans or on the soil. The chemical and physical characteristics of the sludges are highly variable, but in general contain significant levels of heavy metals. Industries are responsible for a portion of this problem, but data indicate that sludges from esentially domestic wastewater sources can also contain substantial amounts of heavy metals (1,2,3). Therefore complete elimination of heavy metals at the source is virtually impossible. It is necessary to assume that heavy metals in sludge will persist and work should progress towards limiting their detrimental effects in addition to removing them. Just the presence of heavy metals in sludge does not mean that toxic effects will occur. The concentration of heavy metal must reach a threshold level and be "available." Availability depends on the chemical specie of the heavy metal present in the sludge. Possible species are listed in Table I. The nature of the heavy metals in sludge will affect their toxicity in the environment. Dotson (4) states that only soluble trace elements are available to plants. It is known that heavy metals are strongly partitioned into the solid phase (suspended solids) fraction of sludges (5, 6). This could be the result of a variety of mechanisms. OBJECTIVE It was the objective of this work to determine if, within the solids fraction, particle size affects heavy metal content. A surface effect may indicate what could be the major mechanism of binding. Soluble metal concentrations indicate if solid phase precipitates and/or complexation is involved. MATERIALS AND METHODS Samples of anaerobically digested sludge were composited from anaerobic digesters. The sources of sludge was a municipal wastewater treatment plant in Keasby, New Jersey which treates a wastewater that is approximately 80% domestic and 20% industrial. The 689
Object Description
Purdue Identification Number | ETRIWC1975059 |
Title | Heavy metal distribution in anaerobically digested sludges |
Author |
Gould, Michael S. Genetelli, Emil J. |
Date of Original | 1975 |
Conference Title | Proceedings of the 30th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,25691 |
Extent of Original | p. 689-699 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-06-29 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page689 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | Heavy Metal Distribution in Anaerobically Digested Sludges MICHAEL S. GOULD, Graduate Assistant EMIL J. GENETELLI, Professor Department of Environmental Sciences Rutgers University New Brunswick, New Jersey 08903 INTRODUCTION Heavy metals in sludges emanating from biological wastewater treatment systems have become a topic of intense interest due to their potential as toxic agents in the environment. These sludges, after anaerobic digestion, are commonly disposed of in landfills, incinerators, oceans or on the soil. The chemical and physical characteristics of the sludges are highly variable, but in general contain significant levels of heavy metals. Industries are responsible for a portion of this problem, but data indicate that sludges from esentially domestic wastewater sources can also contain substantial amounts of heavy metals (1,2,3). Therefore complete elimination of heavy metals at the source is virtually impossible. It is necessary to assume that heavy metals in sludge will persist and work should progress towards limiting their detrimental effects in addition to removing them. Just the presence of heavy metals in sludge does not mean that toxic effects will occur. The concentration of heavy metal must reach a threshold level and be "available." Availability depends on the chemical specie of the heavy metal present in the sludge. Possible species are listed in Table I. The nature of the heavy metals in sludge will affect their toxicity in the environment. Dotson (4) states that only soluble trace elements are available to plants. It is known that heavy metals are strongly partitioned into the solid phase (suspended solids) fraction of sludges (5, 6). This could be the result of a variety of mechanisms. OBJECTIVE It was the objective of this work to determine if, within the solids fraction, particle size affects heavy metal content. A surface effect may indicate what could be the major mechanism of binding. Soluble metal concentrations indicate if solid phase precipitates and/or complexation is involved. MATERIALS AND METHODS Samples of anaerobically digested sludge were composited from anaerobic digesters. The sources of sludge was a municipal wastewater treatment plant in Keasby, New Jersey which treates a wastewater that is approximately 80% domestic and 20% industrial. The 689 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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