29 March 2007Intersol 2007, Paris, France1 Implementation of ISCO in soil remediation: lessons learned Thomas Keijzer PhD, Charles Pijls MSc & Martine.

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Presentation transcript:

29 March 2007Intersol 2007, Paris, France1 Implementation of ISCO in soil remediation: lessons learned Thomas Keijzer PhD, Charles Pijls MSc & Martine van Gool MSc Tauw bv, Deventer, the Netherlands

29 March 2007Intersol 2007, Paris, France2 Tauw? Consultancy firm with offices in six European countries including France (Tauw Environnement in Dijon, Lyon, Douai & Paris) Focus lies on environmental quality & civil engineering Clients are among others (multinational) companies, (local, regional & national) authorities, investors, lawyers So what do my colleagues and I do …?

29 March 2007Intersol 2007, Paris, France3 So what do my colleagues and I do …? Find the best & cost-effective remediation solution for each individual site ISCO Fenton’s steam injection excavation

29 March 2007Intersol 2007, Paris, France4 Introduction Applied in the Netherlands (since 1999), started with Fenton’s reagens currently persulphate is hot Popular it is simple – inject an overdoses strong oxidant, when in contact with a reduced specie e.g. a contaminant complete degradation occurs it is capable of large mass reduction it is fast no above ground waste treatment

29 March 2007Intersol 2007, Paris, France5 Introduction ISCO includes applications of different oxidants, each with its own field of application, contaminant situation, and results that can be achieved Fenton’s reagens (classic & modified) ozone (C-Sparge TM ) ozone/peroxide (Perozone TM ) permanganate persulphate (activated & non-activated) solid peroxides (slow oxygen release compounds, ORC ® )

29 March 2007Intersol 2007, Paris, France6 Fenton’s reagens © In Situ Technieken © Tauw

29 March 2007Intersol 2007, Paris, France7 Fenton’s reagens typically used in source zones short remediation time (<2 yrs) typically 2 injection periods high level of safety required → restricted access Mass removal technique mass removal typically between 70 and >95% target values defined on groundwater concentration e.g. for PCE 40 µg·L –1 are not advisable high concentration in source zone remain after remediation © KBBL

29 March 2007Intersol 2007, Paris, France8 Fenton’s reagens | example PCE injection wells

29 March 2007Intersol 2007, Paris, France9 example shallow monitoring screens deep monitoring screens

29 March 2007Intersol 2007, Paris, France10 Fenton’s reagens | lessons learned Results mass reduction % e.g. 5403; 63,000 → 3,500 µg·L –1 results in monitoring wells not conclusive: favourable e.g. 4004, 4-5; 66,000 → 16,000 µg·L –1 unfavourable soil sampled approx. 1 m from injector 5352 with mass reduction 96%; 34,000 → 1,400 µg·L –1 contained 710 mg·kg –1 PCE mobilisation / displacement due to injection of large volumes soil chemistry – SOD of lesser importance, buffer capacity and Fe(II) availability governing

29 March 2007Intersol 2007, Paris, France11 Ozone & ozone/peroxide © Tauw © Verhoeve Milieu © Tauw

29 March 2007Intersol 2007, Paris, France12 Ozone | C-Sparge TM Ozone continues co-injection of O 3 in an adapted air sparging system typically used in reduction of groundwater plumes … sometimes used in source zones without DNAPL extended remediation time (3-5 yrs) high level of safety required → O 3 production on-site Concentration reduction technique target values defined on groundwater concentrations e.g. for PCE 40 µg·L –1 (or lower) are realistic

29 March 2007Intersol 2007, Paris, France13 Ozone/peroxide | Perozone TM Ozone/peroxide co-injection of O 3 & hydrogen peroxide in an adapted air sparging system typically used in source zones without DNAPL … also used in reduction of groundwater plumes extended remediation time (3-5 yrs) high level of safety required → O 3 production on-site Mass / concentration reduction technique target values defined on groundwater concentrations e.g. for PCE 40 µg·L –1 (or lower) are realistic mass reduction typically 70 and >99%

29 March 2007Intersol 2007, Paris, France14 Ozone/peroxide | example 1 Degradation of Mecoprop, source zone injection period fits based on t½=20 d

29 March 2007Intersol 2007, Paris, France15 example 2 TCE & cDCE source zone (no DNAPL)

29 March 2007Intersol 2007, Paris, France16 Ozone/peroxide | lessons learned Results mass reduction 80 - >95% results in monitoring further down gradient or deeper disappointing (no effect) processes known from air sparging are of importance e.g. radius of influence, convection, preferential (air) flow paths, soil heterogeneity soil chemistry – SOD of lesser importance rule of thumb approx. 15 g O 3 needed per m 3 soil

29 March 2007Intersol 2007, Paris, France17 Permanganate © Tauw

29 March 2007Intersol 2007, Paris, France18 Permanganate typically used in source zones … not cost-effective in plume areas used in low (2-4%) solutions short remediation time (<2 yrs) stable (mild) oxidant → less rebound Mass / concentration reduction technique mass removal typically between 70 and >95% target values defined on groundwater concentration can be used as polishing step after e.g. Fenton’s © Tauw

29 March 2007Intersol 2007, Paris, France19 example TCE & cDCE reduction in source zone (no DNAPL)

29 March 2007Intersol 2007, Paris, France20 Permanganate | example Soil heterogeneity © Tauw !

29 March 2007Intersol 2007, Paris, France21 Results reduction groundwater concentrations sufficient, over-all results disappointing often 2 injection periods necessary soil heterogeneity important parameter soil chemistry – SOD crucial rule of thumb inject excess MnO 4 to overcome all SOD soil reactivity high compared to US references Permanganate | lessons learned (Brown, 2003)

29 March 2007Intersol 2007, Paris, France22 Selection ISCO technique DNAPL? source area nuisance yes time frame no permanganate or ozone/peroxide ozone ozone/peroxide Fenton’s reagens <1 year >1 year issue no issue DNAPL? no yes

29 March 2007Intersol 2007, Paris, France23 Summarising ISCO is not a silver bullet solution → ISCO part of a complete remediation strategy Limiting factors remediation target values → technique and site specific soil heterogeneity → where is the contaminant going? oxidant? → specific soil survey & optimal selection of injection system soil chemistry → do laboratory test on site samples → pilot remediation

29 March 2007Intersol 2007, Paris, France24

29 March 2007Intersol 2007, Paris, France25 Fenton’s reagens | contaminants groupspecific contaminants TPH light TPH-fraction, alkenes heavy TPH-fraction, alkanes CHC PCE, TCE, DCE & VC, chlorobenzenes, chlorophenols Tetra, Chloroform, 111TCA & 112TCA, PCB’s, aromatic compounds BTEX, naphthalene, phenols, light PAH’s (2 / 3-ring) heavy PAH’s (>4-ring) otherMTBE

29 March 2007Intersol 2007, Paris, France26 Ozone & ozone/peroxide | contaminants groupspecific contaminants TPH light TPH-fraction, alkenes heavy TPH-fraction, alkanes CHC PCE, TCE, DCE & VC, chlorobenzenes, chlorophenols Tetra, Chloroform, 111TCA & 112TCA, PCB’s, pesticides (POP’s) aromatic compounds BTEX, naphthalene, phenols, light PAH’s (2 / 3-ring) heavy PAH’s (>4-ring) otherMTBE

29 March 2007Intersol 2007, Paris, France27 Permanganate | contaminants groupspecific contaminants TPH alkenes TPH, alkanes CHC PCE, TCE, DCE & VC, chlorobenzenes, chlorophenols Tetra, Chloroform, 111TCA & 112TCA, PCB’s aromatic compounds toluene, xylenes, phenols benzene PAH’s othercyanides !