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Ameliorative effect of phyto-ash and biogas digestate improvers on soil contaminated with heavy metals

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PL
Remediacyjne działanie polepszaczy z popiołu z biomasy roślinnej oraz pofermentu na glebę zanieczyszczonej metalami ciężkimi
Języki publikacji
EN
Abstrakty
EN
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.
PL
W pracy zastosowano 9 popiołów z biomasy roślinnej: brzozy (Betula), dębu (Quercus), dębu czerwonego (Quercus rubra), grabu (Carpinus), sosny (Pinus sylvestris), topoli (Populus), klonu (Acer), słomy rzepaku (Brassica napus) oraz słomy pszennej (Triticum aestivum), które wymieszano z pofermentem w stosunku 1:1. Otrzymano 9 organiczno-mineralnych polepszaczy glebowych. Koncepcja badań polegała na wyodrębnieniu taniego i środowiskowo przyjaznego polepszacza do remediacji gruntów zdegradowanych. Zanieczyszczone Cu, Zn, Pb and Cd próbki gleb pobrano w strefie zlokalizowanej po południowo-wschodnej stronie Huty Zn i Pb w Miasteczku Śląskim. Popioły z biomasy roślinnej, polepszacze oraz poferment zastosowano w dawkach 0, 5, 10, 20, 40 t∙ha-1. Skuteczność procesu remediacyjnego oceniono przy użyciu testów: 0,11 mola CH3COOH dm--3, pH 3,0 (Reaktywne formy Cu, Zn, Pb, Cd) oraz 0,10 mola NaNO3 dm--3 (formy biodostępne). Spośród wielu zbadanych parametrów, zmiany pH ujawniły, że polepszacze mineralno-organiczne mogą skutecznie zastępować (liniowe R2>0,90****; P<0,001) popioły z biomasy roślinnej w zabiegach remediacyjnych. Właściwości buforowe wyrażone pojemnością wymienną w stosunku do kationów (CEC) poprawiły się progresywnie: 29, 52, 71, 100% (na obiektach z popiołami) oraz: 18, 37, 44, 73% (na obiektach z polepszaczami) odpowiednio dla dawek 5, 10, 20, 40 t∙ha-1, w porównaniu do CEC na kontroli. Wskaźniki dynamicznej skuteczności remediacyjnej (DRE) dla Cu, Zn, Pb i Cd wskazały na specyficzne reakcje geochemiczne zainicjowane popiołami, polepszaczami oraz pofermentem. Dawki 5,0–10,0 t∙ha-1 dla popiołów roślinnych, ok. 20 t∙ha-1 dla polepszaczy [1:1, tzn. popiół:poferment] oraz 10–20 t∙ha-1 pofermentu są zalecane.
Rocznik
Strony
73--83
Opis fizyczny
Bibliogr. 45 poz., tab., wykr.
Twórcy
autor
  • Poznan University of Life Sciences, Poland
  • Poznan University of Life Sciences, Poland
  • Poznan University of Life Sciences, Poland
  • Poznan University of Life Sciences, Poland
autor
  • Poznan University of Life Sciences, Poland
Bibliografia
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  • 8. Ciesielczuk, T., Kusza, G. & Nemś, A. (2011). Fertilization with biomass ashes as a source of trace elements for soils, Environmental Protection and Natural Resources, 49, pp. 219-227. (in Polish)
  • 9. Ciesielczuk, T., Rosik-Dulewska, C. & Kochanowska, K. (2014). The influence of biomass ash on the migration of heavy metals in the flooded soil profile-model experiment, Archives of Environmental Protection, 40, 4, pp. 3-15.
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  • 17. Garg, R.N., Pathak, H., Das, D.K. & Tomar, R.K. (2005). Use of fly ash and biogas slurry for improving wheat yield and physical properties of soil, Environmental Monitoring and Assessment, 107, 1-3, pp. 1-9.
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  • 22. ISO 11466 International Standard (1995). Soil quality-Extraction of trace elements soluble in aqua regia. Geneva.
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  • 25. Madejón, E., Pėrez de Mora, A., Felipe, E., Burgos, P. & Cabrera, F. (2006). Soil amendments reduce trace element solubility in a contaminated soil and allow regrowth of nature vegetation, Environmental Pollution, 139, pp. 40-52.
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  • 37. Stankowski, S. & Maciorowski, R. (2011). Ashes from biomass as a potential source of nutrient elements for plants. In: Seminar “Management of Coal Combustion Products”. Proceedings, pp. 160-180, Warsaw. (in Polish)
  • 38. Stolarski, M.J., Szczukowski, S., Tworkowski, J. & Krzyżaniak, M. (2013). Cost of heat energy generation from willow biomass, Renewable Energy, 59, pp. 100-104.
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  • 44. Wiśniewski, D., Gołaszewski, J. & Białowiec, A. (2015). The pyrolysis and gasification of digestate from agricultural biogas plant, Archives of Environmental Protection, 41, pp. 70-75.
  • 45. Xiao, R., Chen, X., Wang, F. & Yu, G. (2011). The physicochemical properties of different biomass ashes at different ashing temperature, Renewable Energy, 36, pp. 244-249.
Uwagi
Opracowanie rekordu w ramach umowy 509/P-DUN/2018 ze środków MNiSW przeznaczonych na działalność upowszechniającą naukę (2019).
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-f2beea6e-5268-4eaf-85eb-7774fad9cc11
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