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Abstract

Although the utilization of pesticides accounted for the group of persistent organic pollutants was banned years ago, a count of pesticides are still directly or indirectly a source of contamination in Europe. One of them, simazine is still allowed for use in the United States. Aim of this experiment was development of soil remediation method which could be utilized for degradation triazine class pesticides – simazine was an example used. A method for soil remediation based on ozonation processes in fluidized bed was successfully utilized for removal of simazine from contaminated soil. For the study soil highly contaminated with simazine up to the concentration of 0.05% w/w was used. Determination of the pesticide levels in soil was performed using extraction and gas chromatography. The method allowed 80% reduction of pesticide concentration level. The degradation of pesticide was accompanied with changes of physicochemical parameters of soil, i.e., decrease of pH and a increase of nitrates concentration. Despite changes in physicochemical properties of the soil, the developed method proved to be highly effective and can be successfully applied on an industrial scale.

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Authors and Affiliations

Maciej Balawejder
Radosław Józefczyk
Piotr Antos
Marcin Pieniążek
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Abstract

Principles of bioluminescence have been described as well as some examples of the biotests that utilize natural bacterial luminescence for assessment of the effects of environment contamination and remediation have been reviewed. The achievements of the last eight years and a new outlook on using rapid biotests for waters, wastewaters, sediments and soils toxicity investigations have been taken into account.
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Authors and Affiliations

Beata Cwalina
Anna Wiącek-Rosińska
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Abstract

We consider in this work a class of finite dimensional time-varying linear disturbed systems. The main objective of this work is to studied the optimal control which ensures the remediability of a disturbance of time-varying disturbed systems. The remediability concept consist to find a convenient control which bringing back the corresponding observation of disturbed system to the normal one at the final time. We give firstly some characterisations of compensation and in second party we find a control which annul the output of the system and we show also that the Hilbert Uniqueness Method can be used to solve the optimal control which ensure the remediability.Ageneral approachwas given to minimize the linear quadratic problem. Examples and numerical simulations are given.
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Authors and Affiliations

El Mostafa Magri
1
Chadi Amissi
1
Larbi Afifi
1
Mustapha Lhous
1

  1. Fundamental and Applied Mathematics Laboratory, Department of Mathematics and Computer Science, Faculty of Sciences Ain Chock, Hassan II University of Casablanca, B.P.5366-Maârif, Casablanca, Morocco
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Abstract

Solidification/Stabilization (S/S) method with cement as a binder to remediate metals in petroleum sludge has been successfully proven. However, this technique has not yet been explored to remediate organic contaminants since a high concentration of Total Petroleum Hydrocarbon (TPH) was also detected in the sludge. This study focuses on remediating 16 Polycyclic Aromatic Hydrocarbons (PAHs) compounds in raw petroleum sludge with Portland cement as a binder using the S/S method. The initial concentration of 16 PAHs in the raw sludge was first measured before the performance of the S/S method to remediate the PAHs were evaluated. The S/S matrices were tested for leaching behavior and strength after 7 and 28 days by air curing. The leaching test was measured using the Toxicity Characteristics Leaching Procedure (TCLP), and the remaining PAHs concentration in the matrices was analyzed using a Gas Chromatography-Mass Spectrometer (GC-MS). In the raw sludge, all 16 PAHs compounds were below the standard limit except for Benzo(a)anthracene, Benzo(a)pyrene, Dibenzo(ah)anthracene, and Indeno(1,2,3- cd_ pyrene), which are considered as high rings PAHs. The high rings PAHs show lower concentration in leachate than low rings PAHs, which indicates the potential of the S/S method in remediating high rings PAHs. The high sludge ratio in S/S matrices has shown that the percentage strength is increasing, similar to Portland cement. Therefore, this study contributed to the possibility of the S/S method in the remediation of PAHs in petroleum sludge by using only Portland cement as a binder.
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Authors and Affiliations

Noor Faiza Roslee
1
ORCID: ORCID
Nor Amani Filzah Mohd Kamil
1
ORCID: ORCID
Aeslina Abdul Kadir
2
ORCID: ORCID
Abdul Rahim Jalil
3
ORCID: ORCID
Nurhidayah Hamzah
4
ORCID: ORCID
Norazian Mohamed Noor
5
ORCID: ORCID
Andrei Victor Sandu
6
ORCID: ORCID

  1. Universiti Tun Hussien Onn Malaysia, Faculty of Civil Engineering and Built Environment, Batu Pahat, Johor, Malaysia
  2. Universiti Tun Hussien Onn Malaysia, Micro Pollutant Research Centre, Batu Pahat, Johor, Malaysia
  3. Pengerang Refining Company Sdn. Bhd. 81600 Pengerang, Johor Malaysia
  4. Universiti Teknologi MARA Department of Water Resource and Environmental System, 40450, Selangor, Malaysia
  5. Universiti Malaysia Perlis (UniMAP), Faculty of Civil Engineering Technology, 01000 Perlis Malaysia
  6. "Gheorghe Asachi” Technical University, Faculty of Materials Science and Engineering, 700050 lasi, Romania
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Abstract

Nine phyto-ashes from the biomass combustion of birch (Betula), oak (Quercus), red oak (Quercus rubra), horbeam (Carpinus), pine (Pinus sylvestris), poplar (Populus), maple (Acer), oilseed rape straw (Brassica napus) and wheat straw (Triticum aestivum) were blended with a biogas digestate at 1:1 mass ratio to give nine organic-mineral soil improvers. The concept of the research was to outline an eco-friendly and low cost soil improver for remediating degraded lands. These (i.e. phyto-ashes, improvers and the biogas digestate) were applied (0, 5, 10, 20, 40 t·ha-1) to a soil metallurgically contaminated with Cu, Zn, Pb and Cd. Of several tested parameters, pH changes revealed that organic-mineral soil improvers may efficiently replace (linear R2>0.90****, P<0.001) phyto-ashes in soil remedial goals. Buffering properties expressed by the cation exchange capacity (CEC) improved progressively: 29, 52, 71, 100% (phyto-ash treatments) and: 18, 37, 44, 73% (improvers treatments) for the rates 5, 10, 20, 40 t·ha-1, respectively as referred to the control CEC. The Dynamic Remediation Efficiency (DRE) indices for Cu, Zn, Pb, Cd revealed metal-specific geochemical reactions initiated by phyto-ashes, improvers and biogas digestate. The rates 5.0–10.0 t·ha-1 for phyto-ashes and about 20 t·ha-1 for improvers [1:1, i.e. Phyto-ash:Biogas digestate] are recommended. For biogas digestate, the rates 10–20 t·ha-1 were found more efficient.

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Authors and Affiliations

Jean Diatta
Witold Grzebisz
Zbigniew Bzowski
Waldemar Spychalski
Maria Biber
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Abstract

Three different types of Fe(II)-modified natural zeolites were tested as supports in continuous-flow columns for the treatment of Cr(VI) contaminated water. The natural zeolites chosen as support were commercially available Zeosand (80% clinoptilolite), ATZ (79% phillipsite/chabazite), and ZS-55RW (90% Chabazite). All the examined modified zeolites turned out active for hexavalent chromium abatement, lowering its concentration below the European regulation level, even at relatively high flow rates (40 mL/h, linear velocity 15 cm/h). Zeosand, having a broader pH range of stability, was found to be the best one in terms of both Fe(II) uptake (0.54 wt%) and Cr removal (90 mg Cr/Kg zeolite).

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Authors and Affiliations

Antonio Lofù
Piero Mastrorilli
Maria Michela Dell’Anna
Matilda Mali
Raffaello Sisto
Rodolfo Vignola
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Abstract

In the first part of the paper the most often used processes in PRB technology are presented and described. These processes are: redox reactions, pH control, adsorption and biodegradation. They proceed in the reactive materials listed in the table. In the second part of the paper the procedure used in the assessment of possibilities of using PRB technology is presented. It was suggested to use preliminary assessment during the initial stage of the procedure, as it limits the range of the analysis to several most important factors. Moreover,. the conditions of using PRB were described. They can help to decide whether this technology should be accepted or not in the initial stage of the procedure. Such preliminary assessment of possibilities of using PRB was performed for two selected areas of dumping sites located in Upper Silesia, Poland. After accepting the possibilities of using this technology in their area, the types of reactive materials for effective treatment of groundwater were proposed for both of them.
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Authors and Affiliations

Tomasz Suponik
ORCID: ORCID
Marcin Lutyński
ORCID: ORCID
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Abstract

Accidental oil spills at open sea is a common environmental problem. They lead to degradation of sea and shoreline life. In the last ten years there has been an increased interest in bioremediation using the enzymatic activity of the naturally occurring microorganisms. In this work the potential of mixed microbial cultures for biodegradation of crude oil in seawater and sand has been examined. Artificial seawater supplemented with nitrogen and phosphorus was inoculated with cultures isolated from refinery sludge. The same cultures were used for experiments in sand polluted by 5% (v/w) of crude oil. These experiments were performed in sterile and semi-natural (not sterile) conditions to see the degradation potential of isolated cultures, their growth characteristics and possible antagonisms between supplemented microorganisms and natural microflora. During the experiments the oxygen demand, number of bacteria (cfu) and optical density (OD660 ) were monitored. After 14 days of cultivation, the concentration of total petroleum hydrocarbons (TPH) in all samples was measured. All tested cultures had a potential for degradation of hydrocarbons in seawater and sand. After two weeks of experiment, loss of hydrocarbons in seawater polluted with crude oil was between 56.8% (A2 culture) and 64.4% (Al culture). The most effective culture for bioaugmentation of seawater does not have to be the best solution for bioaugmcntation of sand. In sand the best degraders in sterile and semi-natural conditions were found in the mixed cultures isolated from Corinth refinery sludge. For this culture concentration of hydrocarbons in sterile sand was 73.2% lower than in control sample and in non-sterile sand 70.5% lower than in control (sterile sand) without bioaugmentation. Finally, the addition of seawater and fertilizers to sand had also a positive influence on contaminants degradation by naturally occurring microorganisms (48%). Experiments performed with different environments (seawater and sand) and under different conditions (sterilized material and semi-natural conditions) confirmed that cultures should be tested in semi-natural conditions especially when indigenous microflora cans posse's high degradation potential. Allochtonie cultures, very active in sterile conditions, after inoculation to natural environment can even slow down the degradation.
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Authors and Affiliations

Wioletta Przystaś
Nikos Pasadakis
Nicolas Kalogerakis
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Abstract

Technologia przepuszczalnych reaktywnych barier (PRB) należy do metod remediacji wód gruntowych. W technologii tej zanieczyszczenia usuwane są bezpośrednio w warstwie wodonośnej poprzez przepływ skażonego strumienia wód gruntowych przez wypełnioną odpowiednim materiałem (aktywnym) barierę aktywną. W artykule przedstawiono problemy związane z tworzeniem się osadów w żelazie metalicznym stosowanymjako material aktywny technologii PRB. Osady te mogą zmniejszać aktywność materiału i jego zdolność filtracyjną. Tworzeniu się osadów mogą towarzyszyć zmiany pH, potencjału redox oraz stężenia tlenu. Zmiany te były obserwowane w badaniach laboratoryjnych przedstawionych w artykule. Ponadto w artykule przedstawiono i udowodniono następującą zasadę: aby zwiększyć skuteczność działania typu Funnel-and-Gate technologii PRB przez zwiększenie szerokości strefy oczyszczania, stosunek współczynnika filtracji materiału aktywnego do współczynnika filtracji warstwy wodonośnej (k,,,/k,ą) powinien przyjąć wartość 6. Ze względu na tworzenie się osadów w żelazie metalicznym, które mogą zmniejszyć jego zdolność filtracyjną, założono jednak, iż stosunek ten powinien wynosić I O. Wartość ta daje pewność, że zmniejszenie się wartości współczynnika filtracji materiału aktywnego na skutek tworzenia się osadów, nie wpłynie w znaczący sposób na szerokość strefy oczyszczania. Przedstawione rozwiązanie może zapewnić skuteczne i długotrwale oczyszczanie wód gruntowych w typie Funnel-and-Gate technologii PRB.
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Authors and Affiliations

Tomasz Suponik
ORCID: ORCID
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Abstract

There are currently large quantities of heterogeneous contaminated sites and the in-situ thermal conductive heating (TCH) technology have been widely used in soil remediation. Some engineering cases have shown that when soil remediation of heterogeneous sites use TCH technology, the gases carrying contaminants migrate laterally and contaminate clean areas. However, there are relatively few domestic studies on this phenomenon. Some international scholars have confirmed the occurrence of this phenomenon on the laboratory scale, but have not proposed an effective solution to the above scientific question. This study first introduced the heating mechanism and heating process of TCH. Meanwhile, the forms and transformation mechanism of organic contaminants were fully expounded during soil remediation by TCH. In addition, the formation, migration, accumulation, and lateral diffusion of gaseous contaminants were comprehensively reviewed during the in-situ thermal desorption of heterogeneous strata. Finally, arrangement methods of extraction pipes to effectively capture gas are provided for the heterogeneous contaminated soils remediated by TCH. The results of this study will provide theoretical and technical support for in-depth understanding of steam movement in heterogeneous formations and the remediation of heterogeneous contaminated sites by TCH technology.
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Bibliography

  1. Baker, R. & Heron, G. (2004). In-Situ delivery of heat by thermal conduction and steam injection for improved DNAPL remediation.TerraTherm, Inc., Fitchburg USA2004.
  2. Baker, R., Lachance, J. & Heron, G. (2006). In-pile thermal desorption of PAHs, PCBs and dioxins/furans in soil and sediment. Land Contamination & Reclamation, 14(2), pp. 620–624. DOI:10.2462/09670513.731
  3. Biache, C., Mansuy-Huault, L., Faure, P., Munier-Lamy, C. & Leyval, C. (2008). Effects of thermal desorption on the composition of two coking plant soils:impact onsolvent extractable organic compounds and metal bioavailability. Environmental Pollution, 3, pp. 671–677. DOI:10.1016/j.envpol.2008.06.020
  4. Bonnard, M., Devin, S., Leyval, C., Morel, J.L. & Vasseur, P. (2010). The influence of thermal desorption on genotoxicity of multipolluted soil. Ecotoxicology and Environmental Safety, 73, pp. 955–960. DOI:10.1016/j.ecoenv.2010.02.02
  5. Brooks, M.C., Wise, W.R. & Annable, M.D. (1999). Fundamental changes in in situ air sparging how patterns. Groundwater Monitoring & Remediation, 19(2), pp. 105–113. DOI:10.1111/j.1745-6592.1999.tb00211.x
  6. Burghardt, J.M. & Kueper, B.H. (2008). Laboratory study evaluating heating of tetrachloroethylene impacted soil. Groundwater Monitoring & Remediation, 28(4), pp. 95–106. DOI:10.1111/ j.1745-6592.2008.00214.x
  7. Carey, V.P. (2007). Liquid-Vapor Phase-change Phenomena, second ed. Taylor and Francis, New York 2007. Cébron, A., Cortet, J., Criquet, S., Biaz, A., Calvert, V., Caupert, C., Pernin, C. & Leyval, C. (2011). Biological functioning of PAHpolluted and thermal desorption-treated soils assessed by fauna and microbial bioindicators. Research in Microbiology, 162, pp. 896–907. DOI:10.1016/j.resmic.2011.02.011
  8. Chiou, C.T., Porter, P.E. & Schmedding, D.W. (1983). Partition equilibria of nonionic organic compounds between soil organic matter and water. Environmental science & technology, 17, pp. 27–231, DOI:10.1021/es00110a009
  9. Chen, F., Freedman, D.L., Falta, R.W. & Murdochb, L.C. (2012). Henry’slaw constants of chlorinated solvents at elevated temperatures. Chemosphere, 86(2), pp. 156–165. DOI:10.1016/j. chemosphere.2011.10.004
  10. Geistlinger, H., Krauss, G., Lazik, D. & Luckner, L. (2006). Direct gas injection into saturated glass beads: Transition from incoherent to coherent gas flow pattern. Water Resources Research, 42, W07403. DOI:10.1029/2005WR004451
  11. Hegele, P.R. & Mumford, K.G. (2014) Gas production and transport during bench-scale electrical resistance heating of water and trichloroethene. Journal of Contaminant Hydrology, 165, pp. 24–36, DOI:10.1016/j.jconhyd.2014.07.002
  12. Heron, G., Bierschenk, J., Swift, R., Watson, R. & Kominek, M. (2016). Thermal DNAPL source zone treatment impact on a CVOC plume. Groundwater Monitoring & Remediation, 36(1), pp. 26–37. DOI:10.1111/gwmr.12148
  13. Heron, G., Carroll, S. & Nielsen, S.G. (2005). Full-scale removal of DNAPL constituents using steam enhanced extraction and electrical resistance heat. Groundwater Monitoring & Remediation, 25(4), pp. 92–107. DOI:10.1111/j.1745- 6592.2005.00060.x
  14. Heron, G., Lachance, J. & Baker R. (2013). Removal of PCE DNAPL from tight clays using in situ thermal desorption. Groundwater Monitoring & Remediation, 3(4), pp. 31–43. DOI:10.1111/ gwmr.12028
  15. Heron, G., Parker, K., Galligan, J. & Holmes, T.C. (2009). Thermal treatment of 8 CVOC source areas to near nondetect concentrations. Groundwater Monitoring & Remediation, 29(3), pp. 56–65. DOI:10.1111/j.1745-6592.2009.01247.
  16. Hicknell, B.N., Mumford, K.G. & Kueper, B.H. (2018). Laboratory study of creosote removal from sand at elevated temperatures. Contam Hydrol, 219, pp. 40–49. DOI:10.1016/j. jconhyd.2018.10.00
  17. Hiester, U., Muller, M., Koschitzky, H. & Trötschler, O. (2013). In situ thermal treatment for source zone remediation of soil and groundwater. British Medical Journal, 31, pp. 482–484.
  18. Janfada, T.S., Class, H., Kasiri, N. & Dehghani, M.R. (2020). Comparative experimental study on heat-up efficiencies during injection of superheated and saturated steam into unsaturated soil. International Journal of Heat and Mass Transfer, 158, 119235. DOI:10.1016/j.ijheatmasstransfer.2019.119235
  19. Jones, S.F., Evans, G.M. & Galvin K.P. (1999). Bubble nucleation from gas cavities – a review. Adv. Colloid Interfac, 80, pp. 27–50. DOI:10.1016/S0001-8686(98)00074-8
  20. Kueper, B.H. & McWhorter, D.B. (1991). The behaviour of dense, nonaqueous phase liquids in fractured clay and rock. Ground Water, 29(5), pp. 716–728. DOI:10.1111/j.1745-6584.1991. tb00563.
  21. Kunkel, A.M., Seibert, J.J., Elliott, L.J., Kelley, R., Katz, L.E. & Pope, G.A. (2006). Remediation of elemental mercury using in situ thermal desorption(ISTD). Environmental Science & Technology, 40(7), pp. 2384–2389. DOI:10.1021/es050358
  22. Li, K. & Horne, R.N. (2002). A capillary model for geothermal reservoirs. Proceedings of the GRC 2002 Annual Meeting,September 23–25, 2002, Reno, USA: Geothermal Resources Council Trans.
  23. Magdalena. M.K., Mumford, K.G., Johnson, R.L. & Sleep, B.E. (2011) Modeling discrete gas bubble formation and mobilization during subsurface heating of contaminated zones. Advances in Water Resources, 34, PP. 537–549. DOI:10.1016/j. advwatres.2011.01.010
  24. Martin, E.J. & Kueper, B.H. (2011). Observation of trapped gas during electrical resistance heating of trichloroethylene under passive venting conditions. Journal of Contaminant Hydrology, 126, pp. 291–300. DOI:10.1016/j.jconhyd.2011.09.004
  25. Martin, E.J., Mumford, K.G. & Kueper, B.H. (2016). Electrical resistance heating of clay layers in water-saturated sand. Groundwater Monitoring & Remediation, 36(1), pp. 54–61. DOI:10.1111/gwmr.12146
  26. Martin, E.J., Mumford, K.G, Kueper, B.H. & Siemens, G.A. (2017). Gas formation in sand and clay during electrical resistance heating. International Journal of Heat and Mass Transfer, 110, pp. 855–862. DOI:10.1016/j.ijheatmasstransfer.2017.03.056
  27. Mumford, K.G., Martin, E.J. & Kueper, B.H. (2021). Removal of trichloroethene from thin clay lenses by electrical resistance heating: Laboratory experiments and the effects of gas saturation. Journal of Contaminant Hydrology, 243, 103892. DOI:10.1016/J. JCONHYD.2021.103892
  28. Mumford, K.G., Smith, J.E. & Dickson, S.E. (2008). Mass flux from a non-aqueous phase liquid pool considering spontaneous expansion of a discontinuous gas phase. Journal of Contaminant Hydrology, 98, pp. 85–96. DOI:10.1016/j.jconhyd.2008.02.007
  29. Munholland, J.L. (2015) Electrical resistance heating of groundwater impacted by chlorinated solvents in heterogeneous sand. ProQuest Dissertations. Munholland, J.L., Mumford, K.G. & Kueper, B.H. (2016). Factors affecting gas migration and contaminant redistribution in heterogeneous porous media subject to electrical resistance heating. Journal of Contaminant Hydrology, 184, pp. 14–24. DOI:10.1016/j.jconhyd.2015.10.011
  30. Netzeva, T.I., Aptula, A.O., Chaudary, S.H., Duffy, J.C., Schultz, T.W., Schűrmann, G. & Cronin, M.T.D. (2003). Structure-Activity Relationships for the Toxicity of Substituted Poly-Hydroxylated. Benzenes to Tetrahymena Pyriformis: influence of Free Radical Formation. Qsar & Combinatorial Science, 22(6), pp. 575–582.
  31. Nilsson, B., Tzovolou, D., Jeczalik, M., TomaszKasela, T., Slack,W., Klint, K.E., Haeseler, F. & Tsakiroglou, D.C. (2011). Combining steam injection with hydraulic fracturing for the in-situ remediation of the unsaturated zone of a fractured soil polluted by jet fuel. Journal of Environmental Management, 92. DOI:10.1016/j.jenvman.2010.10.004
  32. Oberle. D. & Kluger, M. (2015). In situ remediation of 1, 4-dioxane using electrical resistance heating. Remediation Journal, 25(2), pp. 35–42. DOI:10.1002/rem.21422
  33. O’Carroll, D.M. & Sleep, B.E. (2007). Hot water flushing for immiscible displacement of a viscous NAPL. Journal of Contaminant Hydrology, 91, pp. 47–266. DOI:10.1016/j.jconhyd.2006.11.003
  34. Schwarzenbach, R.P., Gschwend, P.M. & Imboden, D.M. (2003). Environmental Organic Chemistry, JohnWiley &Sons, New Jersey2003. Scriven, L.E. (1959). On the dynamics of phase growth. Chemical Engineering Science, 10, PP. 1–13, DOI:10.1016/0009- 2509(59)80019-1
  35. Sinnott, R.K. (2005). Coulson’s and Richardson’s Chemical Engineering, Chemical Engineering Design. Elsevier Inc., UK2005.
  36. Sleep, B.E. & Ma, Y.F. (1997). Thermal variation of organic fluid properties and impact on thermal remediation feasibility. Journal of Soil Contamination, 6(3), pp. 281–306. DOI:10.1080/15320389709383566
  37. Smith, J.M. & Van Ness, H.C. (1987). Introduction to Chemical Engineering Thermodynamics. Mc-Graw Hill, Inc., New York 1987.
  38. Sun, H., Yang, X.R., Xie, J.Y. & Zhao, Y.S. (2021). Remediation of Diesel-Contaminated Aquifers Using Thermal Conductive Heating Coupled With Thermally Activated Persulfate. Water Air Soil Pollut, 232: 293. DOI:10.1007/s11270-021-05240-x
  39. Suthersan. S.S., Horst. J., Schnobrich. M., Welty, N. & McDonough, J. (2016). Remediation Engineering-Design Concepts Second Edition, CRC Press, Boca Raton 2016.
  40. Tang, S., Wang, X., Mao, Y., Zhao, Y., Yang, H. & Xie, Y.F. (2015). Effect of dissolved oxygen concentration on iron efficiency: removal of three chloroacetic acids. Water Research, 73, pp. 342–352. DOI:10.1016/j.watres.2015.01.02
  41. Triplett Kingston,J.L., Dahlen, P.R. & Johnson, P.C. (2010). State-of- -the-practice review of in situ thermal technologies. Groundwater Monitoring & Remediation, 30 (4), pp. 64–72. DOI:10.1111/ j.1745-6592.2010.01305.x
  42. Triplett Kingston, J.L., Johnson, P.C., Kueper, B.H. & Mumford, K.G. (2014). In situ thermal treatment of chlorinated solvent source zones. Chlorinated Solvent Source Zone Remediation, 7, pp. 509–557.
  43. Udell, K.S. (1996). Heat and mass transfer in clean-up of underground toxic wastes. In Annual Reviews of Heat Transfer, 7, pp. 333–405. DOI:10.1615/AnnualRevHeatTransfer.v7.80.
  44. Vermeulen, F. & McGee, B. (2000). In situ electromagnetic heating for hydrocarbon recovery and environmental remediation. J Can. Pet. Technol, 39(8), pp. 24–28. DOI:10.2118/00-08-DAS
  45. Voort, M., Kempenaar, M., Driel, M., Raaijmakers, M.J. & Mendes, R. (2016). Impact of soil heat on reassembly of bacterial communities in the rhizosphere microbiome and plant disease suppression. Ecology Letters, 19(4), pp. 375–382. DOI:10.1111/ele.12567
  46. Zhao, C., Mumford, K.G. & Kueper, B.H. (2014). Laboratory study of non-aqueous phase liquid and water co-boiling during thermal treatment. Journal of Contaminant Hydrology, 164, pp. 49–58. DOI:10.1016/j.jconhyd.2014.05.008
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Authors and Affiliations

Wei Ji
1
Rong-Bing Fu
1
Cai-Hong Gao
1
Jia-Bin Yao
1

  1. State Key Laboratory of Pollution Control and Resources Reuse,College of Environmental Science and Engineering, Tongji University, Shanghai 200092, ChinaCentre for Environmental Risk Management and Remediation of Soil and Groundwater,Tongji University, Shanghai 200092, China
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Abstract

Sludge from cardboard mill is most commonly landfilled, but it could also be recycled on-site into production or reused in some other way. In this study the use of sludge from cardboard mill as stabilizing agent in the stabilization treatment of cadmium polluted sediment was examined. The effectiveness of treatment and long-term leaching behavior of cadmium was evaluated by determining the cumulative percentage of cadmium leached, diffusion coefficients (De) and by applying different leaching tests (semi-dynamic test, toxicity characteristic leaching procedure, waste extraction test). In order to simulate the “worst case” leaching conditions, the semi-dynamic leaching test was modified using 0.014 M acetic acid (pH = 3.25) and humic acids solution (20 mg l-1 TOC) as leachants instead of deionized water. A diffusion-based model was used to elucidate the controlling leaching mechanisms. Applied treatment was effective in immobilizing cadmium irrespective of high availability in the untreated sample. The controlling leaching mechanism appeared to be diffusion, which indicates that a slow leaching of cadmium could be expected when the cardboard mill sludge as stabilization agent is applied.

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Authors and Affiliations

Milena Becelic
Miljana Prica
Milena Dalmacija
Bozo Dalmacija
Vesna Pesic
Dejan Krcmar
Rastko Milosevic
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Abstract

This article is in a sense a dialogue devoted to the presence of conspiracy theories on social media and mass culture. The authors present the current state of research on the development of digital culture and its social consequences. Next, a case study of the existence of the conspiracy theory of so-called Wielka Lechia is presented. In the analysis the authors combine theoretical and technical considerations of Web 2.0 with research inquiry, which is the analysis of the structure of the Great Lechia theory in social media. The problem of the popularity of the concept of Paweł Szydłowski's and Janusz Bieszk's has been referred to a wider context related to the modern functioning of historical knowledge on the Web. The factual orientation of historical education and the influence of social media on the functioning of the social dimension of history and historians have been indicated as the reason for the current state of the problem. Finally, the authors refer to the digital version of pseudoscience to its earlier analog counterparts and make a structural comparison of both. The effect of this confrontation is to point the phenomenon of remediation of conspiracy theories and the growing deprofessionalization of discourse, which ultimately leads to the end of the era of intellectual authorities.

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Authors and Affiliations

Wiktor Werner
ORCID: ORCID
Adrian Trzoss
ORCID: ORCID
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Abstract

When exposed to high cadmium concentrations applied to the soil, the abiotic stress-tolerant, semi-halophytic C3/CAM (Crassulacean Acid Metabolism) photosynthetic intermediate plant Mesembryanthemum crystallinum L. demonstrates negligible poisoning symptoms with well-protected photochemical activity. Gas exchange analysis of the soil-grown plants exposed to Cd concentrations ranging from 0.01 to 10.0 mM revealed stimulation of net photosynthesis in the C 3 metabolic state, and this observation coincided with an increase in the transpiration level. The obtained results suggest that the initial action of Cd after the administration of this heavy metal is the stimulation of stomata opening.
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Bibliography

[1]. Adams, P., Nelson, D. E., Yamada, S., Chmara, W., Jensen, R. G., Bohnert, H. J. & Griffiths, H. (1998) Growth and development of Mesembryanthemum crystallinum (Aizoaceae). The New Phytologist, 138, 171–190. DOI:10.1046/j.1469-8137.1998.00111.x
[2]. Adamakis, I.-D.S., Sperdouli, I., Hanć, A., Dobrikova, A., Apostolova, E. & Moustakas, M. (2021). Rapid hormetic responses of photosystem II photochemistry of clary sage to cadmium exposure. International Journal of Molecular Sciences, 22, 41. DOI:10.3390/ijms22010041
[3]. Ali, H., Khan, E. & Sajad, M.A. (2013) Phytoremediation of heavy metals – Concepts and applications. Chemosphere, 91, 869–881. DOI:10.1016/j.chemosphere.2013.01.075
[4]. Amari, T., Ghnaya, T., Debez, A., Taamali, M., Ben Youssef, N., Lucchini, G., Sacchi, G.A. & Abdelly, C. (2014). Comparative Ni tolerance and accumulation potentials between Mesembryanthemum crystallinum (halophyte) and Brassica juncea: metal accumulation, nutrient status and photosynthetic activity. Journal of Plant Physiology, 171, 1634–1644. DOI:10.1016/j.jplph.2014.06.020
[5]. Arshad, M., Ali, S., Noman, A., Ali, Q., Rizwan, M., Farid, M. & Irshad, M.K. (2015). Phosphorus amendment decreased cadmium (Cd) uptake and ameliorates chlorophyll contents, gas exchange attributes, antioxidants and mineral nutrients in wheat (Triticum aestivum L.) under Cd stress. Archives of Agronomy and Soil Science, 62(4), 533-546. DOI:10.1080/03650340.2015.1064903
[6]. Björkman, O. & Demming, B. (1987). Photon yield of oxygen evolution and chlorophyll fluorescence characteristics at 77ºK among vascular plants of diverse origin. Planta, 170, 489–504. DOI:10.1007/BF00402983
[7]. Carvalho, M.E.A., Piotto, F.A., Franco, M.R., Rossi, M.L., Martinelli, A.P., Cuypers, A. & Azevedo R.A. (2019). Relationship between Mg, B and Mn status and tomato tolerance against Cd toxicity. Journal of Environmental Management, 240, 84-92. DOI:10.1016/j.jenvman.2019.03.026
[8]. Chibuike, G.U. & Obiora, S.C. (2014). Heavy metal polluted soils: effect on plants and bioremediation methods. Applied and Environmental Soil Science, 1-13. DOI:10.1155/2014/752708
[9]. Cushman, J.C. & Borland, A.M. (2002). Induction of crassulacean acid metabolism by water limitation. Plant Cell & Environment, 25(2), 295-310. DOI:10.1046/j.0016-8025.2001.00760.x
[10]. Dias, M.C., Monteiro, C., Moutinho-Pereira, J., Correia, C., Gonçalves, B. & Santos, C. (2013). Cadmium toxicity affects photosynthesis and plant growth at different levels. Acta Physiologiae Plantarum, 35, 1281-1289. DOI:10.1007/s11738-012-1167-8
[11]. Gallego, S.M., Pena, L.B., Barcia, R.A., Azpilicueta, C.E., Iannone, M.F., Rosales, E.P., Zawoznik, M.S., Groppa, M.D. & Benavides, M.P. (2012). Unravelling cadmium toxicity and tolerance in plants: Insight into regulatory mechanisms. Environmental and Experimental Botany, 83, 33-46. DOI:10.1016/j.envexpbot.2012.04.006
[12]. Gawrońska, K. & Niewiadomska, E. (2015). Participation of citric acid and isocitric acid in the diurnal cycle of carboxylation and decarboxylation in the common ice plant. Acta Physiologiae Plantarum, 37, 61. DOI:10.1007/s11738-015-1807-x
[13]. Gawroński S., Łutczyk G., Szulc W. & Rutkowska B. (2022) Urban mining: Phytoextraction of noble and rare earth elements from urban soils. Archives of Environmental Protection 48(2),24-33 DOI:10.24425/aep.2022.140763
[14]. Haag-Kerwer, A., Schäfer, H.J., Heiss, S., Walter, C. & Rausch, T. (1999). Cadmium exposure in Brassica juncea causes a decline in transpiration rate and leaf expansion without effect on photosynthesis. Journal of Experimental Botany, 50, 1827–1835. DOI:10.1093/jxb/50.341.1827
[15]. Jia, L., Liu, Z., Chen, W., Ye, Y., Yu, S. & He, X. (2015). Hormesis effects induced by cadmium on growth and photosynthetic performance in hyperaccumulator Lonicera japonica Thunb. Journal of Plant Growth Regulation, 34, 13-21. DOI:10.1007/s00344-014-9433-1
[16]. Kholodova, V., Volkov, K. & Kuznetsov, V. (2005). Adaptation of the common ice plant to high copper and zinc concentrations and their potential using for phytoremediation. Russian Journal of Plant Physiology, 52, 748–757. DOI:10.1007/s11183-005-0111-9
[17]. Larsson, F.H., Bornman, J.F. & Asp, H. (1998). Influence of UV-B radiation and Cd2+ on chlorophyll fluorescence, growth and nutrient content in Brassica napus. Journal of Experimental Botany, 49, 1031-1039. DOI:10.1093/jxb/49.323.1031
[18]. Liang, L., Liu,W., Sun, Y., Huo, X., Li, S. & Zhou, Q. (2017) Phytoremediation of heavy metal contaminated saline soils using halophytes: Current progress and future perspectives. Environmental Reviews, 25, 269–281. DOI:10.1139/er-2016-0063
[19]. Lösch, R. & Köhl, K.I. (1999). Plant respiration under influence of heavy metals, [In:] Prasad, M.N.V. & Hagemeyer, J. (Eds): Heavy Metal Stress in Plants. Springer, Berlin, Heidelberg, 139-156.
[20]. Małachowska-Jutsz, A. & Gnida, A. (2015). Mechanisms of stress avoidance and tolerance by plants used in phytoremediation of heavy metals. Archives of Environmental Protection, 41, 4, 104-114. DOI:10.1515/aep-2015-0045
[21]. Moradi, L. & Ehsanzadeh, P. (2015). Effects of Cd on photosynthesis and growth of safflower (Carthamus tinctorius L.) genotypes. Photosynthetica, 53(4), 506-518. DOI:10.1007/s11099-015-0150-1
[22]. Moustakas, M., Moustakas, J. & Sperdouli I. (2022). Hormesis in photosystem II: a mechanistic understanding. Current Opinion in Toxicology, 29, 57-64. DOI:10.1016/j.cotox.2022.02.003[
[23]. Nosek, M., Kaczmarczyk, A., Śliwa, M., Jędrzejczyk, R., Kornaś, A., Supel, P., Kaszycki, P. & Miszalski, Z. (2019). The response of a model C3/CAM intermediate semi-halophyte Mesembryanthemum crystallinum L. to elevated cadmium concentrations. Journal of Plant Physiology, 240, 153005. DOI:10.1016/j.jplph.2019.153005
[24]. Nosek, M., Kaczmarczyk, A., Jędrzejczyk, R.J., Supel, P., Kaszycki, P. & Miszalski, Z. (2020). Expression of genes involved in heavy metal trafficking in plants exposed to salinity stress and elevated Cd concentrations. Plants, 9, 475. DOI:10.3390/plants9040475
[25]. Prasad, M.N.V., Malec, P., Waloszek, A., Bojko, M. & Strzałka, K. (2001). Physiological responses of Lemma trisulca L. (duckweed) to cadmium and copper bioaccumulation. Plant Science, 161, 881-889. DOI:10.1016/S0168-9452(01)00478-2
[26]. Śliwa-Cebula, M., Kaszycki, P., Kaczmarczyk, A., Nosek, M., Lis-Krzyścin, A. & Miszalski, Z. (2020). The common ice plant (Mesembryanthemum crystallinum L.) – phytoremediation potential for cadmium and chromate-contaminated soils. Plants, 9, 1230. DOI:10.3390/plants9091230
[27]. Śliwa-Cebula, M., Koniarz, T., Szara-Bąk, M., Baran A., Miszalski Z. & Kaszycki, P. (2023). Phytoremediation of metal-contaminated bottom sediments by the common ice plant (Mesembryanthemum crystallinum L.) in Poland. Journal of Soils and Sediments, 23, 1065-1082. DOI:10.1007/s11368-022-03401-x
[28]. Tokarz, K., Piwowarczyk, B., Wysocka, A., Wójtowicz, T., Makowski, W. & Golemiec, E. (2019). Response of grass pea (Lathyrus sativus L.) photosynthetic apparatus to short-term intensive UV-A: red radiation. Acta Physiologiae Plantarum, 41, 168. DOI:10.1007/s11738-019-2962-2
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Authors and Affiliations

Adriana Maria Kaczmarczyk
1
ORCID: ORCID
Michał Nosek
2
Paweł Kaszycki
3
ORCID: ORCID
Paulina Supel
3
ORCID: ORCID
Zbigniew Miszalski
1

  1. W. Szafer Institute of Botany, Polish Academy of Sciences, Kraków, Poland
  2. Institute of Biology, University of the National Education Comission Kraków, Poland
  3. Department of Plant Biology and Biotechnology, University of Agriculture in Kraków
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Abstract

The aim of the research was to determine the factors defining the growth and development of Lolium perenne and Trifolium repens upon petroleum contamination. The top layer of clay soil contaminated with petroleum products resulting from an oil pipeline failure was collected for the tests. The control was the same type of uncontaminated soil with the addition of, under laboratory conditions, tissue paper. The research was conducted in two stages. The first concerned the germination process and seedlings parameters (Petri dishes). The germination energy ( GE) and the germination capacity ( GC) of seeds were determined. The seedling’s development was also evaluated based on ‘WinRhizo PRO 2009’ software. Then, in the second stage, pot tests were carried out, where the growth and development of species in the first year after sowing were temporarily measured. The parameters studied were the number, height, green and dry masses of the plants.
A Gompertz regression model describing seed species germination and number species as time dependent dynamic was applied. The data were analysed statistically using variance analysis (ANOVA) and the PCA (principal component analysis) method. The results of our study indicated that admixture of petroleum into the soil does not seriously affect the development dynamics of Lolium perenne seedlings. The diesel oil contamination mostly affects the germination of the Trifolium repens by a statistically significant increase of the maximum value of germination and increasing the maximum growth rate.
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Authors and Affiliations

Bogumiła Pawluśkiewicz
1
ORCID: ORCID
Ilona Małuszyńska
2
ORCID: ORCID
Marcin Małuszyński
1
ORCID: ORCID
Piotr Dąbrowski
1
ORCID: ORCID
Tomasz Gnatowski
1
ORCID: ORCID

  1. Warsaw University of Life Sciences – SGGW, Institute of Environmental Engineering, ul. Nowoursynowska 159, 02-776 Warsaw, Poland
  2. Warsaw University of Life Sciences – SGGW, Water Center, Warsaw, Poland
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Abstract

This article critically evaluates the summary procedure introduced by Protocol No. 14 to the European Convention on Human Rights, adopted within the reform of the European Court of Human Rights system. The summary procedure, now set out in Art. 28(1)b of the Convention, was instituted in order to facilitate expediency and to reduce the case load of the Court. This article argues that while judicial economy is a legitimate goal, the summary procedure under Art. 28(1)b has considerable deficiencies that undermine some of the systemic goals and core values of ECHR law. There is a manifest lack of remedies vis-à-vis the choice of the procedure, choice of applicable law, and no appeals against final decisions rendered in the course of the summary procedure. Notably, the concept of “well-established case-law” seems to be neither clear nor reliable, as evidenced in the cases analysed in the article. These cases, which involve the issue of socially- owned property in Serbia, serve to demonstrate some of the significant errors in interpretation and decision-making which can result from application of the summary procedure.

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Authors and Affiliations

Sanja Djajić
Rodoljub Etinski
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Abstract

The purpose of this article is to determine the relationship between the principles of subsidiarity and effectiveness and an effective remedy for the excessive length of proceedings within the legal order of the European Convention on Human Rights. The article assumes that these key principles of the ECHR’s legal order have an impact on such a remedy, both in the normative and practical dimensions. This assumption has helped explain many aspects of the Strasbourg case law regarding this remedy. Concerning the relationship of this remedy with the principle of subsidiarity, it raises issues such as: the “reinforcing” of Art. 6 § 1; the “close affinity” of Arts. 13 and 35 § 1; and the arguability test. In turn, through the prism of the principle of effectiveness, the reasonableness criterion and the requirement of diligence in the proceedings are presented, followed by the obligations of States to prevent lengthiness of proceedings and the obligations concerning adequate and sufficient redress for such an excessive length of proceedings. The analysis shows that an effective remedy with respect to the excessive length of proceedings is not a definitive normative item, as the Court consistently adds new elements to its complex structure, taking into account complaints regarding the law and practice of States Parties in the prevention of and compensation for proceedings of an excessive length.

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Authors and Affiliations

Elżbieta Morawska

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