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HYDC06  12/5/05  5:34 PM  Page 238






                 238    Chapter Six




























                 Fig. 6.24 Distribution of nitrate concentration in an unconfined medium sand aquifer below a large septic system located on the north
                 shore of Lake Erie, Ontario. The water-table depth below the infiltration pipes of Tile bed 2 is about 1.2 m and is sufficient to allow
                 for almost complete oxidation of the sewage constituents during migration through the sandy vadose zone. After Aravena and
                 Robertson (1998).



                   Other waste water constituents are influenced by  flow, making unsaturated conditions below septic
                 the major changes in redox and pH conditions that  systems desirable for both oxygen supply and patho-
                 occur in the reaction zones of septic systems. Calcite  gen retention.
                 (CaCO ) is often dissolved in drain fields in order to  In terms of hydrophobic organic contaminants such
                      3
                                              +
                 buffer the acidity released during NH oxidation and  as halogenated aliphatics and aromatics, partitioning
                                              4
                                      2+
                 this results in increased Ca  concentrations in the  on to the accumulated organic matter in the septic tank
                 effluent. Other cations may also be released from the  and the drain field will act to retain these contaminants.
                 solid phase during buffering reactions such as mineral  Until recently overlooked, a potential source of
                 dissolution or cation exchange. Wilhelm et al. (1994b)  contamination can arise from cemetery operations.
                 also identified trace metal cations such as Cu, Cr, Pb  Detailed studies within cemeteries in Australia
                 and Zn in concentrations in the range of 2–300 µgL −1  (Knight & Dent 1998; Dent 2002) have principally
                 in many domestic waste waters as a result of the  identified forms of nitrogen but also sodium, mag-
                 changes in redox and pH. Although their specific  nesium, strontium, chloride, sulphate and forms of
                 behaviour in septic systems is less well understood, a  phosphorus as characterizing cemetery groundwa-
                 large fraction of trace metals is likely to be retained in  ters. Cemetery functions are best understood con-
                 particulate matter in the septic tank where they form  ceptually as a special kind of landfill operation that is
                 insoluble sulphides.                        strongly influenced by temporal and spatial variabil-
                   Domestic waste water contains pathogenic bacteria  ity of cemetery practices. Boyd (2002) found that the
                 and viruses and overflow and seepage of waste water  amounts of decomposition products leaving cemet-
                 is a major cause of disease outbreaks associated with  eries are very small and that well-sited and managed
                 groundwater (Craun 1985; Pedley & Howard 1997).  cemeteries have a low environmental impact and
                 Bacteria are retained in septic systems primarily by  are a sustainable activity. The most serious pollution
                 straining in the biological mat; the layer of accumulated  situation is for the escape of pathogenic bacteria or
                 organic matter found directly beneath the distribu-  viruses into the environment. The potential for such
                 tion pipes. In general, the mobility of bacteria and  contamination can only be assessed by a compre-
                 viruses is much greater in saturated than unsaturated  hensive hydrogeological investigation.
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