in situ sanitation congrès inte… · biomass production will be assessed at different time steps...

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Treatment ME thodology and MO nitoring for sequenced R eallocation of severely polluted I ndustrial S ites (MEMORIS) : A combination of innovative technologies In situ Sanitation Monitoring Aude Devalckeneer (1) , Amandine Liénard (2) , Pascal Goderniaux (3) , Marie - Eve Duprez (4) , Liza Niemirowsky (5) , Yves Saintenoy (6) , Vincent Vanderheyden (5) , Marion Bouviez (1) , Jean - Marie Colet (1) , Gilles Colinet (2) , Olivier Kaufmann (3) , Anne - Lise Hantson (4) , Lahcen El Hiki (4) . Project founded by The Walloon Region Greenwin (Belgium) (1) UMONS - Human biology and Toxicology Unit, (2) ULg Department of BIOsystem Engineering, (3) UMONS - Geology and applied geology Unit, (4) UMONS - Chemical and Biochemical processes engineering Unit, (5) SITEREM SA., (6) DUFERCO wallonie SA. Acetylcholine activity Neurotoxicity Acyl-CoA oxydase activity Oxidative Stress Comet Assay Genotoxicity Glutathione-S-transferase activity Detoxification System Bioindicator Models Spectroscopic Method (H 1 -RMN) Metabonomic profile Health Risk Introduction The economic redeployment of the Walloon Region requires the reallocation of many fallow land requiring substantial rehabilitation work. Indeed, sites from old steel industry are the subject of mixed pollution and generally occupy very large surfaces. Therefore, the excavation, transport and storage of contaminated materials become financially and ethically not feasible also involving risks for the health of the residents. The MEMORIS process combines 4 techniques in a unique way and provides innovative and effective solutions for sanitation and in situ monitoring. The remediation - monitoring coupling will constitute a new approach for the management and sequential re - use of highly polluted sites according to toxicological risks . Laboratory studies on mammals are being increasingly the subject of new legislations, it becomes important to implement alternative solutions that respond to the law of the 3Rs (Reduce, Replace, Refine) [4]. Omics approaches allow to reduce the number of organisms as well as a However, mammals species remain largely exploited in biomedical research and in toxicology studies in particular. Invertebrate animal models which are already used in the environmental risk assessment [5] could be transposed from ecotoxicology to the evaluation of health risks. Indeed, many similarities exist between the detoxification systems and the involved pathways. refinement of experiments by using non-invasive methods. The aim of this study is to use invertebrate models in human health risk assement by using mutiple bioindicators and combining a bench of predictive biomarkers. The study is based on predictive biomarkers allowing to integrate different absorption pathways as well as being a global reflect of exposition. The use of mutiple bio-indicators allows to follow the evolution of the effects across seasons and the combination of several biomarkers assures us to cover the most important toxic effects. Bioremediation is the use of living organisms such as bacteria, fungi and algae to decontaminate polluted soil and/or water. Some species are known to be efficient for the biodegradation of polycyclic aromatic compounds (PAHs), among them bacterial strains Pseudomonas sp., Rodococcus sp., Mycobacterium sp. and white rot fungi Phanerochaete chrysosporium or Pleurotus ostreatus are commonly found in litterature as degrading strains [1,2]. MEDIUM (pH, nutrients , temperature , etc. ) POLLUTANTS ( PAHs , BTEX) MICRO - ORGANISMS ( bacteria , fungi) BIOREMEDIATION Several parameters will be studied: - Bioavailability of pollutants (use of surfactants such as Tween or cyclodextrins) - Enzymatic system (increasing production or activity of enzymes involved in the pollutant degradation i.e. lignin peroxidase, manganese peroxidase and laccase) - Influence of soil temperature (soil will be heated using heating pipes or hot water circulation) on micro-organism growth, pollutant bioavailability and bioremediation - Influence of other pollutants present in the polluted soil, especially heavy metals (zinc, Phytoextraction Phytoextraction Phytostabilization Phytodegradation Phytostimulation Phytodegradation Phytoremediation developed under the MEMORIS project aims to (i) degrade organic compounds and (ii) stabilize and extract metal contaminants. To do this, tests will be developed in bins or containers with soil sampled on the site. Each bin will be vegetated with woody species (e.g. willow, poplar or birch) and / or herbaceous (e.g. alfalfa, miscanthus). The effectiveness of technique on soil decontamination and biomass production will be assessed at different time steps (seasonal). Subsequently, phytoremediation technique will be applied to a green unit set up on the MEMORIS site. The substrate of this unit will be composed of a leachate / sand mixture and will be inoculated by a consortium of microorganisms. Phytostabilization as well as phytoextraction will be assessed by monitoring the contents of mobile metals in the substrate and the metal contents present in the biomass produced (stem and leaf). The micro-organisms will allow the biodegradation of organic compounds in support of phyto / rhizo-degradation by plants. In areas with moderate surface pollution of the experimental site, an in situ plantation will be established. The choice of plants will be defined on the basis of the preliminary results obtained by the experimentation in bins (plants survival, vegetation cover, mobile fraction in metals in the soil, metal contents in the leachates and metal concentrations in the biomass). [1] Haritash A.K., Kaushik C.P., Journal of Hazardous Materials 169 (2009) 1-15, [2] Gan S., Lau E.V., Ng H.K., Journal of Hazardous Materials 172 (2009) 523-549, [3] Favas P. J. C. et al., 2014. Phytoremediation of Soils Contaminated with Metals and Metalloids at Mining Areas: Potential of Native Flora, [4] Riley et al., Rapid, responsive, relevant (R3) research : a call for a rapid learning health research enterprise. Clinical and Translational Medicine. 2013; [5] Cortet et al., The use of invertebrate soil fauna in monitoring pollutant effects. Eur. J. Soil Biol. 35, 115-134. 1999. [6] Etienne A. 2014. Amélioration du suivi de la contamination des sols et des eaux souterraines dans le cadre de la gestion des risques environnementaux. Thèse de doctorat en sciences de l’ingénieur. UMONS. [3] Phytovolatilization In the MEMORIS project a consortium of bacterial and/or fungal strains which have the ability to degrade PAHs and BTEX content of the polluted soil at a large scale will be proposed. The selected strains will be either commercial selected strains and/or indigenous strains isolated from the polluted site (soil and/or water). cadmium, lead, nickel, chrome, etc.), which can interfere with thebioremediation process (inhibition of enzymatic system, inhibition of micro-organisms growth) - Identification of bioremediation products (are the obtained compounds safer than original PAHs/BTEX or are they worse?) "Electrical resisitivity section showing variations in the subsurface electrical resistivities along a profile. This section results from the inversion of electrical resistivities carried out with electrodes spreaded". The objective is to develop geophysical techniques, for imaging the evolution of the contaminant plume under stimulated biodegradation as well as the subsurface temperature, continuously in space and time. The biodegradation of pollutants is stimulated by the injection of nutrients, and by the increase of the subsurface temperature with external intakes of heat. This part of the research project covers several aspects: (1) Design and implementation in the field of the monitoring system using hydrogeophysical techniques; (2) Acquisition, processing and interpretation of the measured data; (3) Field sampling to calibrate and validate the methods; (4) Numerical modeling of flow and heat transfers. 0.00 10.0 30.0 50.0 70.0 90.0 150 250 48.8 60.8 0 3 6 9 12 0 36.8 24.8 12.8 Electric geophysical methods are sensitive to changes in the electrical properties of soils and groundwater that are affected by the presence of contaminants. This follow-up allow to extend, at low cost, interpretations derived from chemical analyzes on water and soil sampling [6]

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Page 1: In situ Sanitation Congrès Inte… · biomass production will be assessed at different time steps (seasonal). Subsequently, phytoremediation technique will be applied to a green

Treatment MEthodology and MOnitoring for sequenced Reallocation of severelypolluted Industrial Sites (MEMORIS) :

A combination of innovative technologies

In situ Sanitation

Monitoring

Aude Devalckeneer (1), Amandine Liénard (2), Pascal Goderniaux (3), Marie-Eve Duprez (4), Liza Niemirowsky (5), Yves Saintenoy (6), Vincent Vanderheyden (5), Marion Bouviez (1), Jean-Marie Colet (1), Gilles Colinet (2), Olivier Kaufmann (3), Anne-Lise Hantson (4), Lahcen El Hiki (4).

Project founded by The Walloon Region – Greenwin (Belgium)

(1) UMONS - Human biology and Toxicology Unit, (2) ULg – Department of BIOsystem Engineering, (3) UMONS - Geology and applied geology Unit, (4) UMONS - Chemical and Biochemical processes engineering Unit, (5) SITEREM SA., (6) DUFERCO wallonie SA.

Acetylcholine activity

Neurotoxicity

Acyl-CoA oxydase activity

Oxidative Stress

Comet Assay

Genotoxicity

Glutathione-S-transferase activity

Detoxification System

Bioindicator Models Spectroscopic Method (H1-RMN)

Metabonomic profile

Health Risk

IntroductionThe economic redeployment of the Walloon Region requires the reallocation of many fallow land requiring substantial rehabilitation work. Indeed, sites from old steel industry are the subject of mixed pollution and generally occupy very large surfaces. Therefore, the excavation, transport and storage of contaminated materials become financially and ethically not feasible also involving risks for the health of the residents. The MEMORIS process combines 4 techniques in a unique way and provides innovative and effective solutions for sanitation and in situ monitoring. The remediation - monitoring coupling will constitute a new approach for the management and sequential re - use of highly polluted sites according to toxicological risks.

Laboratory studies on mammals are being increasingly the subject of newlegislations, it becomes important to implement alternative solutions thatrespond to the law of the 3Rs (Reduce, Replace, Refine) [4].Omics approaches allow to reduce the number of organisms as well as a

However, mammals species remain largely exploited in biomedical research and in toxicologystudies in particular. Invertebrate animal models which are already used in the environmental riskassessment [5] could be transposed from ecotoxicology to the evaluation of health risks. Indeed,many similarities exist between the detoxification systems and the involved pathways.

refinement of experiments by using non-invasive methods.

The aim of this study is to use invertebratemodels in human health risk assement by usingmutiple bioindicators and combining a bench of

predictive biomarkers.

The study is based on predictive biomarkers allowing to integrate different absorption pathways aswell as being a global reflect of exposition. The use of mutiple bio-indicators allows to follow theevolution of the effects across seasons and the combination of several biomarkers assures us tocover the most important toxic effects.

Bioremediation is the use of living organisms such as bacteria, fungi and algae to decontaminatepolluted soil and/or water. Some species are known to be efficient for the biodegradation ofpolycyclic aromatic compounds (PAHs), among them bacterial strains Pseudomonas sp., Rodococcussp., Mycobacterium sp. and white rot fungi Phanerochaete chrysosporium or Pleurotus ostreatus arecommonly found in litterature as degrading strains [1,2].

MEDIUM(pH, nutrients,

temperature, etc.)

POLLUTANTS(PAHs, BTEX)

MICRO-ORGANISMS

(bacteria, fungi)

BIOREMEDIATION

Several parameters will be studied:

- Bioavailability of pollutants (use of surfactantssuch as Tween or cyclodextrins)

- Enzymatic system (increasing production oractivity of enzymes involved in the pollutantdegradation i.e. lignin peroxidase, manganeseperoxidase and laccase)

- Influence of soil temperature (soil will beheated using heating pipes or hot watercirculation) on micro-organism growth, pollutantbioavailability and bioremediation

- Influence of other pollutants present in thepolluted soil, especially heavy metals (zinc,

Phytoextraction

Phytoextraction

Phytostabilization Phytodegradation

Phytostimulation

Phytodegradation

Phytoremediation developed under theMEMORIS project aims to (i) degradeorganic compounds and (ii) stabilize andextract metal contaminants. To do this, testswill be developed in bins or containers withsoil sampled on the site. Each bin will bevegetated with woody species (e.g. willow,poplar or birch) and / or herbaceous (e.g.alfalfa, miscanthus). The effectiveness oftechnique on soil decontamination andbiomass production will be assessed atdifferent time steps (seasonal).

Subsequently, phytoremediation techniquewill be applied to a green unit set up on theMEMORIS site. The substrate of this unitwill be composed of a leachate / sandmixture and will be inoculated by aconsortium of microorganisms.

Phytostabilization as well as phytoextraction will be assessed by monitoring the contents ofmobile metals in the substrate and the metal contents present in the biomass produced (stemand leaf). The micro-organisms will allow the biodegradation of organic compounds in support ofphyto / rhizo-degradation by plants.

In areas with moderate surface pollution of the experimental site, an in situ plantation will beestablished. The choice of plants will be defined on the basis of the

preliminary results obtained by the experimentation in bins (plants survival,vegetation cover, mobile fraction in metals in the soil, metal contents inthe leachates and metal concentrations in the biomass).

[1] Haritash A.K., Kaushik C.P., Journal of Hazardous Materials 169 (2009) 1-15, [2] Gan S., Lau E.V., Ng H.K., Journal of Hazardous Materials 172 (2009) 523-549, [3] Favas P. J. C. et al., 2014. Phytoremediation of Soils Contaminated with Metals and Metalloids at Mining Areas: Potential of Native Flora, [4] Riley et al., Rapid, responsive, relevant (R3) research : a call for a rapid learning health research enterprise. Clinical and Translational Medicine. 2013; [5] Cortet et al., The use of invertebrate soil fauna in monitoring pollutant effects. Eur. J. Soil Biol. 35, 115-134. 1999. [6] Etienne A. 2014. Amélioration du suivi de la contamination des sols et des eaux souterraines dans le cadre de la gestion des risques environnementaux. Thèse de doctorat en sciences de l’ingénieur. UMONS.

[3]

Phytovolatilization

In the MEMORIS project a consortium of bacterial and/or fungalstrains which have the ability to degrade PAHs and BTEX contentof the polluted soil at a large scale will be proposed. Theselected strains will be either commercial selected strainsand/or indigenous strains isolated from the polluted site (soiland/or water).

cadmium, lead, nickel, chrome, etc.), which can interfere with thebioremediationprocess (inhibition of enzymatic system, inhibition of micro-organisms growth)- Identification of bioremediation products (are the obtained compoundssafer than original PAHs/BTEX or are they worse?)

"Electrical resisitivity section showing variations in the subsurface electrical resistivities along a profile. This section results from the inversion of electrical resistivities carried out with electrodes spreaded".

The objective is to develop geophysical techniques, for imaging the evolutionof the contaminant plume under stimulated biodegradation as well as the subsurfacetemperature, continuously in space and time. The biodegradation of pollutants is stimulated by theinjection of nutrients, and by the increase of the subsurface temperature with external intakes ofheat.

This part of the research project covers several aspects:(1) Design and implementation in the field of the monitoring system using hydrogeophysical

techniques;(2) Acquisition, processing and interpretation of the measured data;(3) Field sampling to calibrate and validate the methods;(4) Numerical modeling of flow and heat transfers.

0.00 10.0 30.0 50.0 70.0 90.0 150 250

48.8 60.8

0

3

6

9

12

0 36.824.812.8

Electric geophysical methods are sensitive to changes in the electricalproperties of soils and groundwater that are affected by the presence ofcontaminants.

This follow-up allow to extend, atlow cost, interpretations derivedfrom chemical analyzes on waterand soil sampling

[6]