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SU0002201
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Entry Properties
Last modified
10/26/2020 3:37:38 PM
Creation date
9/4/2019 6:43:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0002201
PE
2626
FACILITY_NAME
UP-99-22
STREET_NUMBER
690
Direction
W
STREET_NAME
FREWERT
STREET_TYPE
RD
City
LATHROP
ENTERED_DATE
10/23/2001 12:00:00 AM
SITE_LOCATION
690 W FREWERT RD
QC Status
Approved
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SJGOV\wng
Supplemental fields
FilePath
\MIGRATIONS\F\FREWERT\690\UP-99-22_-94-14\SU0002201\CDD OK.PDF
Tags
EHD - Public
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t3loresN t'cchnologv 52(1995) I01-107 <br /> yMElsevier Science Limited <br /> LllEat <br /> Printed in at Britain.All rights reserved <br /> f19(0-8521/95/h9j0 <br /> ' 'BEVIEH 0960-8524(94)00144-8 R V, 51-52 <br /> ORGANIC LINERS FOR THE SEALING OF EARTHEN <br /> RESERVOIRS <br /> S. F. Barrington," R. Stilborn`' & R. Garcia Moreno" <br /> -nniml Engineering Delwnment of McGill University, 21 111 Lakeshore Road, Ste Anne ele Bellevue, H9X 3V9, Canada <br /> "Lakeside lndusiries, Brooks, Alberni, T1R lBR Canada <br /> (Received 27 July 1994; revised version received 25 November 1994; accepted 5 December 1994) <br /> .tstract contained in the liquid deposit themselves at the <br /> "til laboratory columns are used to test the sealing entrance to, and within, the soil pores. This physical <br /> etency of organic liners made of various combing_ scaling process can be enhanced by microbes pro- <br /> ; 3ns of straw and eiJe✓ Lcc1:c: mantdre or broiler during gums and by biochemical reactions i <br /> 6a In tests conducted in triplicate each liner was destroying the soil pores (Barrington et al., 1987; <br /> *d at the centre of a 0.6 m core of loam and Rowscll et al., 1985; Davis et a[., ]973). <br /> *erged for 83 days under 3.25 m of low total solids Consequently, wastewater will effectively seal a <br /> ,M wastewater. The liquid and contaminant seepage- soil as long as it contains at least 4% TS (Barrington <br /> &e for each liner was monitored throughout the et al., 1990) and the soil has a fine particle-size <br /> eameru. The finer made of 85%a beefiot manure distribution. High proportions of coarse particles <br /> 15% straw, on a dry matter basis, gave the lowest (sands and gravels) lead to larger soil pores and <br /> t' ge rate of 19 x 10-9 in s-'. This same liner fim- leaching, rather than trapping, of the wastewater <br /> %nitrogen <br /> solid particles.-', To ensure physical clogging, Barring- <br /> seepage rates well below 06 g in d is the limit required by most North American ton and Broughton (1988) have sugggested <br /> amental Authorities. Extrapolation of the seep- minimum soil clay-particle contents of 5 and 15% <br /> "rates, which .still decreased after 83 slays, indicated for manures produced by ruminants and monogas- <br /> 'fiu the best liner could reach sealing levels of tric animals, respectively. Hills (1976) found that <br /> q 10-'m s-' after 128 days clogging requires a soil with at least 9% clay particle <br /> content and with a limited particle size over 0 5 mm. <br /> words: Liners, wastewater, low total solids, glei- Otherwise, physical scaling may not limit seepage <br /> : n rates under the required level of 1 x 10-` m s- and <br /> the earthen reservoir can contaminate the surround- <br /> ing groundwater. <br /> ODUCTION Enhanced gleization is a technique which has <br /> n structures for the storage of wastewater are <br /> been used to seal soils expc;ed to wastewater of low <br /> mical and environmentally safe if they are TS (Nlcholaichuk, 1978). This process requires a <br /> t according to specific design criteria. One of water-logged soil with a minimum organic matter <br /> ikse criteria requires that the wastewater contains content. Under such conditions, specific anaerobic <br /> �1ore than 4% TS (total solids) to initiate a physical <br /> microbes reduce the medium and solubilize impor- <br /> 5!ialing process. Low total solids problems can be tant soil aggregation cements such as magnesium <br /> 6n6lved through the impermeabilization of the soil and iron compounds. As a result, the soil loses its <br /> dj enhancedg leization. This technique consists of structure, its permeability and its large pores (Rus- <br /> sell, 1988; Mirtskhulava et al., 1972). <br /> -"ng a layer of er�ani- mntter at, a depth of <br /> °x'315-030 in under the soil surface to be submerged. Enhanced gleization has been used to seal earthen <br /> irrigation channels as well as reservoirs (Mirtskhu <br /> organic layer brings about a microbial cedar- <br /> - <br /> iAbo process, thereby destroying the structure and lava et al., 1972). The technique requires the burial <br /> iii acing the permeability of the soil. An experiment of an organic- layer of 3-4 kg m_z of dry matter <br /> �Oconducted to test the sealing ability of enhanced some 0.15-0.30 in below the soil surface. Once sub- <br /> 'enation through the use of organic liners made of merged and under ambient temperatures ranging <br /> us mixtures of straw and either beellot manure between 10 and 30°C, a plastic soil layer develops to <br /> 'broiler litter. a depth of 30-50 mm after 4-8 weeks, 150-200 mm <br /> e sealing of soils by wastewater depends mostly after 1 year, and 300-350 mm after 3-4 years. To <br /> :rb a physical process whereby the solid particles effectively induce gleization Mirtskhulava et al. <br /> 101 <br />
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