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Ps ' <br /> ~� It would seem that neutrall�arl®n Liquids In Landfills:The Federal Regulatory History t; <br /> of acids and bases prior to their Prior to May 1980 No regulations concerning the disposal of;I' <br /> disposal would be the best landfills. <br /> safeguard against clay liner May 1980 EPA promulgated regulations to prohibit t' <br /> failure /n these Cases unless the ment of bulk or containerized liquid waste <br /> resulting salts have an adverse fills. , <br /> effect on the !/Hers. November 1981 Rules promulgated May 19.- 1980, wen <br /> effect. 2€; <br /> February 1982 EPA suspended the prohibition of landfill-I" <br /> of bulk or containerized liquids. <br /> permeabilities in excess of I x 10-' March 1982 EPA, responding to the public outcry promp. <br /> cm/sec prior to the passage of one pore the February action, promulgated an intern <br /> volume. The calcareous smectitic soil (effective on the same date) prohibiting the <br /> exceeded this permeability within 1.5 disposal of containerized liquids unless all fr ' <br /> pore volumes (Fig. 2C) Density to vis- uid is removed, absorbed, solidified or oth. <br /> cosity ratio of acetone (2.4) indicates eliminated. <br /> that permeability to acetone should in- July 1982 EPA promulgated interim final rules that;(lj, <br /> crease 240% over values obtained with tinued the rule promulgated in March of 198 <br /> water. Observed permeabilities for the containerized liquids and (2) stated bulk liq <br /> acetone permeated soils exceeded must not be placed in landfills unless the facili <br /> 1000% of the permeabilities to water. equipped with a liner and leachate collection <br /> While illitic and calcareous smectitic tem. <br /> clay soils were 100 fold (10,000%) Leachates can be generated in landfills ing for the liners. Rather,he feels' <br /> more permeable, the noncalcareous even with no burial of bulk or contai- designers and operators can rely ort <br /> smectic clay soil was 1000 fold nerized liquids. This happens when ei- manufacturer's specifications.Or <br /> (100,000%) more permeable to acetone ther (a) the waste's own liquid content water monitoring of the new sites u' <br /> than water. separates from the waste or(b)surface required if a double liner is used.' <br /> It is interesting to note that all soils water or groundwater which has infil- single liner is used, however, gro <br /> treated with acetone has initial perme- trated the landfill passes through the water monitoring is required. Lose <br /> ability decreases. These decreases con- waste. Ther ►re, even though EPA's detection and collection systems will`, <br /> tinued until passage of ^:0.5 pore vol- new rules covering existing and new required in the double-lined facili <br /> ume. During passage of the next 0.5 hazardous waste landfills, issued in which do not monitor groundwa <br /> pore volume, however the soils under- July 1982,ban the burial of free liquids Says Cook, "If a leak is detected, <br /> went large permeability increases. in containers, and bulk liquids without groundwater monitoring would be' <br /> Initial permeability decreases were a liner and leachate collection system, .quired if corrective action is not to <br /> thought to be caused by the higher leachate can still be generated and will when the leak is discovcro.°' <br /> dipole moment of acetone relative to have to be collected. What the new regulations don't da;i� <br /> water, while the subsequent permeabil- In existing clay-lined landfills, while place significantly more attention Cq <br /> ity increases may have been due to the groundwater monitoring is now re- preventing leachate generation t <br /> higher molecular weight of acetone rel- quired, testing liner permeability has existed in past practice;instead iia« <br /> lative to water.Changing the liquid in a against expected leachates, as recom- chates are expected to be collected at <br /> clay soil to one with a higher dipole mended in this article, is not. In a tele- treated when they are discovered. <br /> moment tends to cause swelling and phone call to EPA's RCRA Hotline, The new EPA rules may eventuali <br /> thereby decrease the permeability of a CE was told it would be "wise" to test be superseded in part by legislati <br /> soil. Changing the liquid to one with a clay liners for permeability but not Sen. Gary Hart, D-Colo., has intr <br /> higher molecular weight tends to cause required. If the waste does migrate, duced a bill requiring EPA to begin jbil <br /> l <br /> shrinking and hence increases the per- EPA pointed out, the site would be eli- process of moving to alternative me <br /> meability of a soil. Examination of the gible for action under RCRA and Su- ods of toxic waste disposal. The soil after acetone treatment showed ex- perfund. would require EPA to draw up a listensive shrinkage and cracking. Such For new facilities, according to Mi- the most dangerous hazardous was <br /> soil shrinkage is usually associated with chael Cook, deputy director of EPA's and would prohibit landfill disposadehydration, indicating that acetone Office of Solid Waste,the synthetic lin- those wastes until methods of render <br /> may have extracted water from soil ers that will henceforth be required them harmless can be certified by th <br /> particle surfaces. must be compatible with the wastes agency. CE will report on the progr <br /> Permed. ' ties of the four clay soils to that are being disposed. He does not of this bill as it moves through the Se <br /> m anol all t creased to values greater believe that this will mean special test- ate.—T.W. and A.M. <br /> an I x 10.7 ig. 213). Unlike acetone, <br /> ffiethanol­lfas a lower dipole moment <br /> than water and consequently caused no <br /> initial 'permeability decrease. Since the soils showed steady permeability Permeabilities of the four clay soils to <br /> particle migration was not detected in inerea_jes to values 10 fold or 1000% xylene are shown in Fig.2E.Permeabil-' <br /> the methanol treated soils, soil piping (kaolinitic soil) and 1'00 fold or ity changes due to the density to viscos <br /> was discounted as the mechanism for 10,000% (illitic and noncalcareous ity ratio of xylene to water (1.07) <br /> the observed permeability increases. If smectitic soils) of permeability values accounts for only a 7% increase in per- <br /> these increases were due solely to the obtained with water. Examination of meability. Actual permeability of the <br /> 1.46 density to viscosity ratio of metha- the methanol permeated soils revealed soils to xylene averaged 100 fold or <br /> nol to water, permeability of the soils the development of large pores and 10,000% of the values obtaindd with <br /> would have leveled out at values 146% cracks visible in the sflrface oI tTie" water. A possible cause of the perme- <br /> of those obtained with water. Instead, soils. ---ability increases was seen in the strut <br /> 68 Civil Engineering-ASCE September 1902 <br /> i <br />