Search results

Filters

  • Journals
  • Authors
  • Keywords
  • Date
  • Type

Search results

Number of results: 41
items per page: 25 50 75
Sort by:
Download PDF Download RIS Download Bibtex

Abstract

There is a need for quality control of wastewater introduced into drainage systems. Physical and chemical analyses of wastewater inform only about the situation existing at the moment of sampling. The analysis based on bioindication methods allows to evaluate the existing state before sampling and so to recognize a drop of excessive loads or harmful substances for activated sludge. This refers to the moment preceding the sample taking at least by the generation time of the species with the lowest reproduction rate. For these reasons, the possibility of using microfauna representatives (feeding on organic pollutions) for bioindication was evaluated. The estimation was made of the usefulness of indicator species from the Kolkwitz-Marssori system, the Shannon-Wiener index based on species abundance and the latter based on abundances of morphological-functional organism groups. The study results showed that the ShannonWiener index calculated for morphological-functional groups (easiest to determine) was accurate enough for bioindication.
Go to article

Authors and Affiliations

Grzegorz Łagód
Jacek Malicki
Agnieszka Montusiewicz
Mariola Chomczyńska
Download PDF Download RIS Download Bibtex

Abstract

Sewage sludge from municipal wastewater treatment plants is currently a serious environmental problem, given its diversity due to the variability of time and heavy metal content. Current research on the monitoring of heavy metals is based on the determination of Pb, Cd, Hg, Ni, Zn, Cu and Cr. This makes any thallium content data difficult to access. The study estimated the degree of contamination of sewage sludge with thallium. The sludge samples came from a sewage treatment plant located in Poland. The results are presented for the total concentration of thallium and its mobile forms. These samples were analyzed by differential pulse voltammetry. The results showed that the average thallium content was 0.203 μg/g and its mobile form was 0.025 μg/g. The conducted research shows that almost 13% of thallium from sewage sludge can be gradually released into the environment.
Go to article

Bibliography

  1. Ahumada, I., Escudero, P., Ascar, L., Mendoza, J.& Richter, P. (2004). Extractability of Arsenic, Copper, and Lead in Soils of a Mining and Agricultural Zone in Central Chile. Communications in Soil Science and Plant Analysis, 35, pp. 1615-1634. DOI:10.1081/CSS-120038558
  2. Alvarez-Ayuso, E., Otones, V., Murciego, A., Garcia-Sanchez, A. & Santa Regina, I. (2013). Zinc, cadmium and thallium distribution in soils and plants of area impacted by sphalerite-bearing mine wastes. Geoderma, 207-208, pp. 25-34. DOI:10.1016/j.geoderma.2013.04.033
  3. Council Directive of 21.III.1991 concerning urban wastewater treatment. 91/271/EEC.
  4. De La Rochebrochard, S., Naffrechoux, E., Drogui, P., Mercier, G. & Blais, J. (2013). Low frequencyultrasound-assisted leaching of sewage sludge for toxic metal removal, dewatering and fertilizingproperties preservation. Ultrasonics Sonochemistry, 20, pp. 109-117. DOI:10.1016/j.ultsonch.2012.08.001
  5. Dmowski, K., Kozakiewicz, A. & Kozakiewicz, M. (2002). Bioindication thallium search in southern Poland. Kosmos, 51(2), pp. 151–163. (in Polish)
  6. Finkelman, R. (1999). Trace elements in coal. Environmental and health significance. Biological Trace Element Research, 67(3), pp. 197–204. DOI:10.1007/BF02784420 .
  7. Frankowski, M., Zioła-Frankowska A., Kowalski, A. & Siepak., J. (2010). Fractionation of heavy metals in bottom sediments using Tessier procedure. Environmental Earth Sciences, 60, pp. 1165-1178. DOI:10.1007/s12665-009-0258-3
  8. Fytili, D. & Zabaniotou, A. (2008). Utilization of sewage sludge in EU application of old and new methods a review. Renewable and Sustainable Energy Reviews, 12 (1), pp. 116-140. DOI: 10.1016/j.rser.2006.05.014
  9. Galván–Arzate, S. & Santamaria, A. (1998). Thallium toxicity. Toxicology Letters, 99(1), pp. 1–13. DOI:10.1016/s0378-4274(98)00126-x
  10. Ibragimow, A., Głosińska., G., Siepak, M. & Walna, B. (2010). Heavy metals in fluvial sediments of the Odra river flood plains-introductory research. Quaestiones geographicae, 29, pp. 37-47. DOI:10.2478/v10117-010-0004-7
  11. Kowalik, R,, Gawdzik, J., Gawdzik. B. & Gawdzik, A. (2020). Analysis of the mobility of heavy metals in sludge for the sewage treatment plant in Daleszyce. Structure and Environment, 12, 85 DOI: 10.30540/sae-2020-010
  12. Larner, B., Seen, A. & Townsend, A. (2006). Comparative study of optimized BCR sequential extraction scheme and acid leaching of elements in the certified reference material NIST 2711. Analytica Chimica Acta, 556, pp. 444-449. DOI:10.1016/j.aca.2005.09.058
  13. Łukaszewski, Z., Jakubowska, M., Zembrzuski, W., Karbowska, B. & Pasieczna,A. (2010). Flow – injection differential pulse anodic stripping voltammetry as a tool for thallium monitoring in the environment. Electroanalysis, 22 (17-18), pp. 1963-1966. DOI:10.1002/elan.201000151
  14. Lukaszewski, Z., Karbowska, B., Zembrzuski, W. & Siepak, M. (2012). Thallium in fractions of sediments formed during the 2004 tsunami in Thailand. Ecotoxicology and Environmwntal Safety, 80, pp. 184-189. DOI:10.1016/j.ecoenv.2012.02.026
  15. Madrid, F., Reinoso, R., Florido, M., Barrientos, E., Ajmone - Marsan, F., Davidson, C. & Madrid, L. (2007). Estimating the extractability of potentially toxic metals in urban soils: A comparison of several extracting solutions. Environmental Pollution, 147, pp. 713-722. DOI:10.1016%2Fj.envpol.2006.09.005
  16. Merrington, G., Oliver, I., Smernik., R. & McLaughlin, M. (2003). The influence of sewage sludge properties on sludge-borne metal availability. Advances in Environmental Research, 8, pp.21-36. DOI:10.1016/S1093-0191(02)00139-9
  17. Pathak, A., Dastidar, M. & Sreekrishnan, T. (2009). Bioleaching of heavy metals from sewage sludge: A review. Journal of Environmental Management, 90, pp. 2343-2353. DOI:10.1016/j.jenvman.2008.11.005
  18. Querol, X., Fernandez-Turiel, J. & Lopez-Soler, A. (1995). Trace elements in coal and their behaviour during combustion in a large power station. Fuel, 74(3), pp. 331–343. DOI:10.1016/0016-2361(95)93464-O
  19. Quevauviller, Ph. (2002). SM&T activities in support of standardization of operationally defined extraction procedures for soil and sediment analysesd, [In] Ph. Quevauviller (ed.), Methodologies in soil and sediment fractionation studies. Single and sequential extraction procedures, European Commission, DG Research, Brussels, Belgium, pp. 1–9.
  20. Regulation of the Minister of the Environment (Rozporządzenie Ministra Środowiska z dnia 6 lutego 2015 r. w sprawie komunalnych osadów ściekowych. Dz.U. 2015 poz. 257)
  21. Regulation of the Minister of the Environment dated. 1.8.2002r. on municipal sewage sludge, Acts. Laws No. 134, item 1140.
  22. Resolution of the Council of Ministers of Polish Government No 233, 29.12.2006.
  23. Smith, K., Fowler, G., Pullket, S. & Graham, N. (2009). Sewage sludge-based adsorbents: A review of their production, properties and use in water treatment applications. Water Research, 43, pp. 2569-2594. DOI:10.1016/j.watres.2009.02.038.
  24. Svancara, I., Ostapczuk, P., Arunchalam, J., Emons, H.E. & Vytras, K. (1997). Determination of thallium in environmental samples using potentiometric stripping analysis. Method development, Electroanalysis, 9(1), pp. 26-31. DOI:10.1002/elan.1140090108
  25. Szarek, Ł. (2020). Leaching of heavy metals from thermal treatment municipal sewage sludge fly ashes. Archives of Environmental Protection, 46(3), pp. 49–59. DOI:10.24425/aep.2020.134535
  26. Vanek, A., Chrastny, V., Komarek, M., Penizek, V., Teper, L., Cabala, J. & Drabek, O. (2013). Geochemical position of thallium in soils from a smelter-impacted area. Journal of Geochemical Exploration, 124, pp. 176-182. DOI:org/10.1016%2Fj.gexplo.2012.09.002
  27. Vanek, A., Komarek, M., Vokurkova, P., Mihaljevic, M., Sebek, O., Panuskova, G., Chrastny, V. & Drabek, O. (2011). Effect of illite and birnessite on thallium retention and bioavailability in contaminated soils. Journal of Hazardous Materials, 191, pp. 170-176. DOI:10.1016/j.jhazmat.2011.04.065
  28. Viraraghavan, T. & Srinivasan, A. (2011). Thallium: Environmental Pollution and Health Effects, Encyclopedia of Environmental Health, pp. 325-333. DOI:10.1016/B978-0-444-52272-6.00643-7
  29. Woźniak, M., Żygadło, M. & Latońska, J. (2004). Assessing the Chemical Stability of Sewage Sludges Deposited Landfills under Natural Conditions. Ochrona Środowiska, 26, pp. 25-31.
  30. Xiao, T., Guha, J., Boyle, D., Liu, C. & Chen, J.(2004). Environmental concerns related to high thallium levels in soils and thallium uptake by plants in southwest Guizhou, China. Science of The Total Environment, 318(1-3), pp. 223-244. DOI:10.1016/S0048-9697(03)00448-0
  31. Zitko, V. (1975). Toxicity and pollution potential of thallium, The Science of the Total Environment, 4, pp. 185-192. DOI:10.1016/0048-9697(75)90039-X
Go to article

Authors and Affiliations

Bożena Karbowska
1
ORCID: ORCID
Włodzimierz Zembrzuski
1
ORCID: ORCID
Joanna Zembrzuska
1
ORCID: ORCID

  1. Poznan University of Technology, Faculty of Chemical Technology, Poland
Download PDF Download RIS Download Bibtex

Abstract

The aim of the study was to estimate the effect otthe composting process in the container technology Kneer on E. coli inactivation. The bacteria placed in the special carriers were introduced into the composted material. The elimination rate of E. coli differed depending on both the carriers· location in the biomass and the thermal conditions. The most effective hygienization, nr the material was noticed in summer - after 48 h in the middle layer, 6 days in the top layer and 10 days in the bottom layer. In spring and autumn, the bacteria survived the longest in the bottom layer - 85 and 45 days, respectively. Apart from the high temperature, the research points out the action of other factors such as competition, antagonism and antibiosis.
Go to article

Authors and Affiliations

Beata Szala
Zbigniew Paluszak
Download PDF Download RIS Download Bibtex

Abstract

Przedmiotem dwuletnich badań było poznanie dynamiki rozwoju wybranych grup drobnoustrojów (mikroorganizmy oligotroficzne, kopiotroficznc, proteolityczne, celulolityczne, rozpuszczające fosforany) w glebie nawożonej komunalnymi osadami ściekowymi. Celem przeprowadzonego doświadczenia było wyjaśnienie możliwości zachwiania równowagi biologicznej gleby, przejawiającej się wzmożonym i długotrwałym rozwojem analizowanych grup drobnoustrojów w glebie, po wprowadzeniu do niej materii organicznej w formic osadów ściekowych, w różnych dawkach. W doświadczeniu zastosowano cztery obiekty badawcze: kontrola-gleba + NPK, 2 Mg s.m. osaduha+rok' + NPK, 4 Mg s.m. osadu-hal-rok' + NPK oraz 8 Mg s.m. osaduhatrok' + NPK). Fosfor i potas stosowano przedsiewnie pod orkę, natomiast azot: część przedsiewnie i drugą część pogłównie. Osady ściekowe stosowano przedsiewnie. Poletka glebowe, na których przeprowadzono badania obsiano żytem odmiany Wibro (2003 r.) oraz obsadzono ziemniakami odmiany Bila (2004 r.). Wykazano, że zastosowane dawki osadów ściekowych nic wpływały istotnie statystycznie na namnażanie się mikroorganizmów glebowych. Na podstawie przeprowadzonych analiz mikrobiologicznych stwierdzono, że w badanym okresie (2003-2004) liczebność oznaczonych grup drobnoustrojów ulegała wahaniom, zależnym od terminu pobierania próbek glebowych. Próbki glebowe, niezbędne do przeprowadzenie analiz, pobierane były w lenninach związanych z kolejnymi fazami rozwojowymi roślin. Kolejnym czynnikiem wpływającym na dynamikę rozwoju mikroorganizmów glebowych był gatunek rośliny użytej w doświadczeniu. Żyto uprawiane w 2003 r. stymulowało rozwój większości grup drobnoustrojów (mikroorganizmów oligotroficznych, kopiotroficznych, proteolitycznych, rozpuszczających fosforany). Z kolei ziemniaki w okresie rozwoju generatywnego ( 16.07- 28.08.2004) spowodowały silniejszy rozwój mikroorganizmów celulolitycznych.
Go to article

Authors and Affiliations

Agnieszka Wolna-Maruwka
Download PDF Download RIS Download Bibtex

Abstract

This work presents results of the release of polycyclic aromatic hydrocarbons (PAH) from granules composed of fly ashes, which are the product of hard and coal combustion and sewage sludge. 3 types of granulates by a weight ratio of ash to sludge 3:7 and 1: 1 were used. The research of PAH leaching was conducted within a simulated period of 24 months, with the examination of PAH washing out every three months. The highest amounts of PAH (297 - 330 μg/kg dw.) were obtained_from granulates containing 7 parts by weights of sewage sludge (3 times higher in comparison with the granulate containing ash and sludge in ratio of I: 1 ). The maximum PAH release from all the examined granulates took place in the 9th month of the research. Benzo(k)fluoranthene revealed the highest fraction (67.4-76.0%) of all examined compounds.
Go to article

Authors and Affiliations

Czesława Rosik-Dulewska
ORCID: ORCID
Urszula Karwaczyńska
Tomasz Ciesielczuk
ORCID: ORCID
Download PDF Download RIS Download Bibtex

Abstract

The main objective of presented research work was the assessment of the impact of reduced straw content, as organic carbon source, on the course of sewage sludge composting process. During the research work performed in industrial conditions, the composting process going in periodically overturned windrows differing in proportion of dehydrated sludge, straw and structural material being 4:1:1 and 8:1:2 respectively, was observed. The consequence of increase of sludge concentration with relation to straw was decrease of C:N ratio in the input material from 11.5 to 8.5. The following parameters were analyzed as indicators for the assessment of the composting process: contents of fulvic acids (FA), humic acids (HA), lignin, cellulose and hemicellulose as well as absorbance in UV/VIS (λ=280, 465 and 665 nm) range. The results obtained have indicated that the increase of sludge content extends the elevated temperature (T>50°C) period from 42 days to approximately 65 days. Our tests did not confirm that limitation of straw content added to sewage sludge had any adverse effect on the course of composting. PI index (HA/FA), which qualifies the compost as mature in the first case – No 1, exceeds limit value of 3.6 on the 83rd day whereas, in the second case No 2, on the 48th day.
Go to article

Authors and Affiliations

Robert Sidełko
1
Bartosz Walendzik
1
Małgorzata Smuga-Kogut
1
Beata Janowska
1
Kazimierz Szymański
1
Anna Głowacka
2
Aleksandra Leśniańska
1

  1. Koszalin University of Technology, Poland
  2. West Pomeranian University of Technology Szczecin, Poland
Download PDF Download RIS Download Bibtex

Abstract

The paper contains a micobiological characteristic of sewage sludge composted in controlled conditions together with bio-wastes (straw, sawdust, bark). An experiment was carried out in which the composted material was mixed up in adequate weight proportion and placed in biorcactor chambers with a constant air flow. The composting process aimed at defining the development dynamics and the survival of pathogenic microorganisms in the sewage sludge composted with different additions in a cybernetic bioreactor. Samples of compost necessary for microbiological analyses were taken at the same time, in reference to the actual temperature value. Bacteriological studies were carried out on selected substrates by plate method determining the number of pathogenic bacteria from the species: Salmonella, Clostridium perfringens, as well as from Enterobacteriaccac family. In the experiments, the presence of living eggs or intestinal ATT pathogens was determined by floatation method, as well. Il was found that the sewage sludge used in composting process did not contain any Salmonella spp. bacteria or any living eggs of intestinal ATT pathogens. Composting process completely eliminated the number or bacteria from Enterobactcriaccae family, bul it did not contribute lo the elimination of Clostridium perfringens bacteria. On the basis of the obtained results, it was found that the elimination of the studied groups of microorganisms, in all studied composts took place with the increase of temperature. In the case or Enterobacteriaceae, it was found that their complete removal from the composted material took place in chamber K3, while in the remaining chambers, it followed 48 hours later. Elimination ofthe vegetative forms ofC!oslridium perfringens bacteria followed after 96 hours of composting, in all composts at the same time. The obtained composts met the sanitary norms according lo the regulations of the EC Commission No. I 85/2007 of February 20, 2007 which changed the regulation of WE No. 809/2003 and WE No. 810/2003 referring to the extension of the validity period of transitional means for composting plants and biogas producing plants according to the instruction orWE No. 1774/2002 of European Parliament and Council and according to the instruction of the Minister for Agriculture and Country Development (2004).
Go to article

Authors and Affiliations

Agnieszka Wolna-Maruwka
Jacek Dach
Download PDF Download RIS Download Bibtex

Abstract

Anaerobic digested sludge supernatant is rich in phosphates and ammonia nitrogen. Phosphates can be almost completely removed in the process of struvite precipitation. Simultaneously, if only magnesium is supplied, usually only a minor part of ammonia equivalent to phosphates will be removed. Increase in pH to about 8.5 or above leads to the presence of free ammonia which affects the struvite crystals form. The possibility of additional ammonia removal with an external or internal source of phosphates was also accounted for. The final product (precipitate) could be considered as a "biofertilizer" or "biosoil" in connection to the technology applied.
Go to article

Authors and Affiliations

Jan Suschka
Sebastian Popławski
Download PDF Download RIS Download Bibtex

Abstract

The goal of the study was to determine the risk posed to soil, groundwater and plants by the application of sewage sludge from a mechanical-biological wastewater treatment plant of nominal capacity of 46 000 m3/d. as fertilizer. Soil samples were collected from an agricultural and vegetable production farm. The leaching experiment was carried out in PCV lizymeters (with percolation water outlet). With respect to the chemistry and biology, the analyzed sludge meets the standards set up for sludge used for agricultural purposes. After 8, 16 and 24 weeks of simulated leaching with atmospheric precipitation, the lecheate from lizymeters showed changes in pH (increasing tendency), electrolytic conductivity (decreasing tendency) as well as slightly lowering content of heavy metals. Heavy metal speciation in sewage sludge showed that they occur in forms of compounds sparingly releasable to the soil solution (fractions III, IV, V). The analysis of sequential chemical extraction carried out in soil with applied sewage sludge, after 24 weeks treatment with simulated atmospheric precipitation doses showed similar heavy metal occurrence tendency as in the case of pure sludge. The total heavy metal content in fractions I-III amounted from 18,6% for Cr to 44,8% for Zn. The remaining content of heavy metals was basically bound with fraction V, which is completely unavailable for plants.
Go to article

Authors and Affiliations

Czesława Rosik-Dulewska
ORCID: ORCID
Mirosław Mikszta
Download PDF Download RIS Download Bibtex

Abstract

Badania nad poziomym rozmieszczeniem makrozoobentosu piaszczystego dna w okolicach Jastarni i Juraty prowadzone były jednorazowo latem 2004 roku. Wyznaczono 15 stanowisk w okolicach Juraty dzieląc stanowiska na cztery promienie oddalone od siebie o 100 m oraz 4 stanowiska w pobliżu portu w Jastarni. Bezkręgowce denne na tym obszarze reprezentowane były przez 18 gatunków i 3 grupy ponadgatunkowe, które w pobliżu Juraty osiągały zagęszczenie X = 1840 osobn. · nr' i masę mokrą X = 121,8 g,,,,;m·', a w okolicach Jastarni x = 638 osobn.im? i x = 376,6 g,,,,,,·m·'. Najczęściej spotykanymi gatunkami były Hediste diversicolor, Cerastoderma g!aucum i Hydrobia u/vae. Większą bioróżnorodnością wyznaczoną wskaźnikiem ShannonaWienera charakteryzowały się stanowiska najbardziej oddalone od brzegu w Juracie. Skład gatunkowy oraz struktura jakościowo-ilościowa fauny dennej w tej części Zatoki Puckiej świadczy o niezadowalającym stanie środowiska oraz niskiej wartości tych obszarów jako miejsca żerowania ryb.
Go to article

Authors and Affiliations

Krystian Obolewski
Anna Jarosiewicz
Download PDF Download RIS Download Bibtex

Abstract

Agricultural utilization of appropriately stabilized sewage sludge appears to be the most rational method of its utilization, even though there is no agreement among scientists as to the impact that these wastes can exert on the maintenance of the soil biological balance. That is why the objective of the performed field-laboratory experiments was to determine the developmental dynamics of selected groups of microorganisms in a grey-brown podzolic soil fertilized with acceptable and unacceptable doses of sewage sludge and farmyard manure. Numbers of six groups of microorganisms were determined at various dates associated with the development of spring barley (total bacterial number, number of actinomycetes, fungi, bacteria from the Azotobacter genus and Pseudomonas j/uorescens) as well as pathogenic bacteria from the Sa/111011ella genus. The selected groups of microorganisms were determined on selective media by the plate method. The obtained research results showed that, in the majority of cases, the applied levels of organic fertilization did not have a significant impact on the numbers of microorganisms in the soil. Therefore, it can be said that the application of both acceptable and unacceptable doses of sewage sludge in the form of fertilizers failed to disturb the biological balance of the examined soil. In addition, the results of the performed experiments indicated that the agricultural utilization of sewage sludge should be forestalled by a sanitation process (e.g. composting) in order to get rid of' pathogenic bacteria, especially bacteria from the Salmonella genus.
Go to article

Authors and Affiliations

Agnieszka Wolna-Maruwka
Aleksandra Sawicka
Download PDF Download RIS Download Bibtex

Abstract

The paper presents microbiological characteristics of sewage sludge derived from the mechanicalbiological sewage treatment plant and farmyard manure as well as composts manufactured from them. In the performed experiment, four types of composts were analyzed. The first of them comprised the sewage sludge alone, the second one - was made up only of farmyard manure, while the remaining composts were prepared by mixing the above-mentioned bio-wastcs in the following proportions: 75% sewage sludge+ 25% farmyard manure and 50% sewage sludge + 50% farmyard manure. The next stage of experiments involved analyses of the composts incubated with soil. The following assays were carried out in the experimental composts and mixtures of soil and composts: counts of Salmonella sp., E. coli, Clostridium perfringens, total counts of bacteria, fungi and actinomycetes on selective media employing the plate method. The performed investigations revealed that the composting process resulted in complete riddance of the Salmonella sp. and reduction in the numbers of the remaining groups of microorganisms. Therefore, it can be said that the composted sewage sludge was suitable for the utilization for agricultural purposes in accordance with the Directive of the Minister of Agriculture and Rural Development of October 2004. Moreover, it was found that, as early as 60 days after the introduction of composts into the soil, counts of the majority of the analyzed groups of microorganisms (with the exception of actinornycctcs and E. coli), including pathogenic bacteria from the C. perfringens genus, were found reduced. The obtained research results proved that the introduction of bi o-wastes into the soil may decrease survivability in the natural environment of certain pathogens; hence it is a good method of utilization of this organic material.
Go to article

Authors and Affiliations

Agnieszka Wolna-Maruwka
Jacek Czekała
Download PDF Download RIS Download Bibtex

Abstract

Deposits used as fertilizer bring to soil both biogens necessary for plant growth and other ingredients such as metals. including heavy metals. Knowledge of quantities and rate in which heavy metals are to be released to soil from granulates is important because of their toxic influence on plants (in the case of high metals concentration). This paper presents results of investigation of elution of Cu. Zn, Ni, Cd, Pb. and Cr from granulates prepared from municipal sewage sludge, hard coal ash and brown coal ash. Elution to water solution was carried out in static conditions with single-stage and tree-stage extraction. Heavy metal a component of sludge-ash granulates eluted in various quantities, i.e. from trace for cadmium to 9.26-9.53 mg/kg of d.m. for zinc. Among the soluble forms of metals the most mobile are (in decreasing sequence): Cu > Pb> Zn> Ni in granulates containing brown coal ash and Cu> Pb> Ni> Zn in granulates contain hard coal ash.
Go to article

Authors and Affiliations

Czesława Rosik-Dulewska
ORCID: ORCID
Katarzyna Głowala
Urszula Karwaczyńska
Jolanta Robak
Download PDF Download RIS Download Bibtex

Abstract

The present work focuses on problems connected with the location and sampling method for pecton (biofilm) in sewage treatment plants. We also discuss the amount and quantity of pecton necessary to compose a representative sample. Comparisons of other selected contamination indicators in place of pecton sampling, are also presented. Research carried out at the WWTP "Hajdow" demonstrated that everything (starting from grid chambers), coming into contact with sewage surfaces is covered with biofilm This biological formation does not cause any significant changes in sewage quality due to its relatively small surface compared to the sewage flux. As presented in the following analysis, pecton can be used for bioindication of sewage quality. This is possible because the organisms forming these communities use substances contained in flowing sewage as nutritional substrates. In such cases the wastewater purification level in biological sewage treatment plants can, in a way similar to rivers, be determined based on bioindication methods using existing similarities between the prevailing processes and organisms.
Go to article

Authors and Affiliations

Grzegorz Łagód
Henryk Sobczuk
ORCID: ORCID
Download PDF Download RIS Download Bibtex

Abstract

In the present paper changes of polycyclic aromatic hydrocarbons (PAHs) content were evaluated during composting of sewage sludge stabilized with coal fly ash. The content of PAHs in sewage sludge used for composting was I 0385 μg/kg (±830). In fly ash only three PAHs were determined (phenanthrene - 0.9 μg/kg, anthraccnc - 1.9 μg/kg and chrysenc - 2.7 μg/kg). Addition of fly ash to composted sewagesludge had various - dependent on its share - effect on PAHs mineralization. Relatively best degradation (66.3%) was noted when sewage sludge was mixed with fly ash in amount 20% (w/w). In composted sewage sludge and sludge with 30% addition of fly ash a decrease of PAH content was also observed (38 and 32.4% respectively). Relatively "best" mineralization was noted for 3-ring PAHs. Estimated half-lives of all investigated compounds depended on individual PAHs properties and ranged from 59 to 1164 days.
Go to article

Authors and Affiliations

Patryk Oleszczuk
Stanisław Baran
Download PDF Download RIS Download Bibtex

Abstract

In Poland, in recent years, there has been a rapid accumulation of sewage sludge – a by-product in the treatment of urban wastewater. This has come about as a result of infrastructure renewal, specifically, the construction of modern sewage treatment plants. The more stringent regulations and strategic goals adopted for modern sewage management have necessitated the application of modern engineering methodology for the disposal of sewage sludge. One approach is incineration. As a consequence, the amount of fly ash resulting from the thermal treatment of municipal sewage sludge has grown significantly. Hence, intensive work is in progress for environmentally safe management of this type of waste. The aim of the experiment was to evaluate the possibility of using the fly ash that results from municipal sewage sludge thermal treatment (SSTT) as an additive to hardening slurries. The article presents the technological and functional parameters of hardening slurries with an addition of fly ash obtained by SSTT. Moreover, the usefulness of these slurries is analyzed on the basis of their basic properties, i.e., density, contractual viscosity, water separation, structural strength, volumetric density, hydraulic conductivity, compressive and tensile strength. The research on technological and functional properties was carried out, the aim of which was to determine the practical usefulness of the hardening slurries used in the experiment. Subsequently, leaching tests were performed for heavy metals in the components, the structure of the hardening slurries. An experiment showed leaching of hazardous compounds at a level allowing their practical application. The article presents the potential uses of fly ash from SSTT in hardening slurry technology.
Go to article

Bibliography

  1. Asavapisit, S., Naksrichum, S. & Harnwajanawong, N. (2005). Strength, lechability, and microstructure characteristics of cement-based solidified plating sludge. Cement and Concrete Research 35, pp. 1042–1049.
  2. Batchelor, B. (2006). Overview of waste stabilization with cement. Waste Management 26, pp. 689–698.
  3. Bobrowski, A., Gawlicki, M. & Małolepszy, J. (1997). Analytical Evaluation of Immobilization of Heavy Metals in Cement Matrices, Environmental Science & Technology, 31, 3, pp. 745-749.
  4. Chang, F.C., Lin, J.D., Tsai, C.C. & Wang, K.S. (2010). Study on cement mortar and concrete made with sewage sludge ash. Water Science and Technology, 62, 7, pp. 1689-1693, 2010.
  5. Chiang, K. Y., Chou, P. H., Hua, C. R., Chien, K. L. & Cheeseman, C. (2009). Lightweight bricks manufactured from water treatment sludge and rice husks. Journal of hazardous materials. 171 (1-3), pp. 76-82.
  6. Chou, J.-D., Wey, M.-Y. & Chang, S.-H. (2009). Evaluation of the distribution patterns of Pb, Cu and Cd from MSWI fly ash during thermal treatment by sequential extraction procedure. Journal of Hazardous Materials 162 (2–3), pp. 1000–1006.
  7. Elicker, C., Sanches Filho P.J. & Castagno K.R.L. (2014). Electroremediation of heavy metals in sewage sludge. Braz. J. Chem. Eng. Sao Paulo, 31(2), pp. 365–371.
  8. EN 450-1:2012. (2012). Fly ash for concrete. Definition, specifications and conformity criteria.
  9. Falaciński, P. (2012). Possible applications of hardening slurries with fluidal fly ashes in environment protection structures. Archives of Environmental Protection. 38, 3, pp. 91-104. DOI: 10.2478/v10265-012-0031-7.
  10. Falaciński, P. & Szarek, Ł. (2016).Possible Applications of Hardening Slurries with Fly Ash from Thermal Treatment of Municipal Sewage Sludge in Environmental Protection Structures. Archives of Hydro-Engineering and Environmental Mechanics, 63, 1, pp. 47–61. DOI: 10.1515/heem-2016-0004
  11. Gawdzik, J. & Latosińska, J. (2014). Assessment of sewage sludge incineration fly-ash heavy metal immobilization. Engineering and Protection of Environment, t. 17, vol. 3, pp. 415-421.
  12. Guo, B., Liu, B., Yang, J. & Zhang, S. (2017).The mechanisms of heavy metal immobilization by cementitious material treatments and thermal treatments: A review. Journal of environmental management, 193, pp. 410-422.
  13. Hoi, K. L., Barford, J.P. & Makay, G. (2010). Utylization of Incineration Waste Ash Residues in Portland Cement Clinker, Chemical Engineering Transaction, 21, pp. 757-762.
  14. Ibragimow, A., Głosińska, G., Siepak, M. & Walna, B. (2010). Preliminary studies of heavy metal pollution in floodplain sediments. Works and Geographic Studies 44, pp. 233–247.
  15. Jakob, A., Stucki ,S. & Kuhn, P. (1995). Evaporation of heavy metals during the heat treatment of municipal solid waste fly ash. Environmental Science and Technology 29, pp. 2429–2436.
  16. Jama-Rodzeńska, A., Bocianowski, J. & Nowak, W. (2014). Impact of municipal sewage sludge on heavy metal content in the sprouts of Salix viminalis L. clones. ZPPNR 576, pp. 45–56. (in Polish)
  17. Kledynski, Z. & Rafalski, L. (2009). Hardening slurries, Warszawa, KILiW PAN, IPPT PAN.(in Polish)
  18. Le Forestier, L. & Libourel, G. (2008). High temperature behavior of electrostatic precipitator ash from municipal solid waste combustors. Journal of Hazardous Materials 154 (1–3) pp. 373–380.
  19. Li, Z. & Shuman, L.M. (1996). Redistribution of forms of zinc, cadmium and nickel in soils treated with EDTA. Sci Total Environ 191, pp. 95–107.
  20. Łukawska, M. (2014). Speciation analysis of phosphorous in sewage sludge after thermal incineration. Inżynieria i Ochrona Środowiska, 17 (3), pp. 433-439 (in Polish)..
  21. Marcinkowski, T. (2004). Alkaline stabilization of municipal sewage sludges. Scientific Papers of the Institute of Environment Protection Engineering of the Wroclaw University of Technology No. 76, Poland.
  22. Nowaka, B., Rochaa, S.F., Aschenbrennerb, F., Rechbergerb, H. & Wintera, F. (2012). Heavy metal removal from MSW fly ash by means of chlorination and thermal treatment: Influence of the chloride type. Chemical Engineering Journal 179 pp. 178– 185.
  23. Petruzzelli, G., Szymura, I., Lubrano,L. & Pezzarossa, B. (1989). Chemical speciation of heavy metals in different size fractions of compost from solid urban wastes. Environetal Technology Letter. 10, pp. 521 – 526.
  24. Polowczyk, I., Bastrzyk, A., Sawiński, W., Koźlecki, T., Rudnicki, P., Sadowski, Z. & Sokołowski, A. (2010). Sorption properties of fly ash from coal burning. Chemical Engineering and Apparatus, 49(1), pp. 93–94.
  25. Poluszyńska. J. & Ślęzak, E. (2015). Characteristics of biomass incineration ashes and the assessment of their possible use for natural purposes. Scientific Works of Institute of Ceramics and Building Materials. 23, pp. 71-78.
  26. Renbo, Y., Wing-Ping, L. & Pin-Han, W. (2012). Basic characteristics of leachate produced by various washing processes for MSWI ashes in Taiwan, Journal of Environmental Management, 104, pp. 67-76.
  27. Rodríguez, N. H., Ramírez, S. M., Varela, M. B., Guillem, M., Puig, J., Larrotcha, E. & Flores, J. (2010). Re-use of drinking water treatment plant (DWTP) sludge: characterization and technological behaviour of cement mortars with atomized sludge additions. Cement and Concrete Research, 40(5), pp. 778-786.
  28. Rosik-Dulewska, Cz. (2001). The content of fertilizer ingredients and heavy metals with their fractions in municiapl waste composts. Problem Journals of Advances in Agricultural Sciences 477, pp. 467-477.
  29. Sánchez-Chardi, A. (2016). Biomonitoring potential of five sympatric Tillandsia species for evaluating urban metal pollution (Cd, Hg and Pb). Atmospheric Environment, 131, pp. 352-359.
  30. Sørum, L., Frandsen-Flemming, J. & Hustad, J. E. (2008). On the fate of heavy metals in municipal solid waste combustion part I: devolatilisation of heavy metals on the grate. Fuel, 82 (18) pp. 2273–2283.
  31. Struis, R.P.W., Ludwig, C., Lutz, H. & Scheidegger A.M. (2004). Speciation of zinc in municipal solid waste incinerator fly ash after heat treatment: an X-ray absorption spectroscopy study. Environmental Science and Technology, 38, pp. 3760–3767.
  32. Szarek, Ł. (2020). Leaching of heavy metals from thermal treatment municipal sewage sludge fly ashes. Archives of Environmental Protection, 46, 3, pp. 49-59, DOI:10.24425/aep.2020.134535.
  33. Szarek, Ł., Falaciński P. & Wojtkowska, M. (2018). Immobilization of selected heavy metals from fly ash from thermal treatment of municipal sewage sludge in hardening slurries, Archives of Civil Engineering, 64, 3, pp.131-144. DOI:10.2478/ace-2018-0034.
  34. Szarek, Ł. & Wojtkowska, M. (2018). Properties of fl y ash from thermal treatment of municipal sewage sludge in terms of EN 450-1. Archives of Environmental Protection 44, 1, pp. 63–69. DOI:10.24425/118182.
  35. Teixeira, S. R., Santos, G. T. A., Souza, A. E., Alessio, P., Souza, S. A. & Souza, N. R. (2011). The effect of incorporation of a Brazilian water treatment plant sludge on the properties of ceramic materials. Applied Clay Science, 53(4), pp. 561-565.
  36. Ure, A.M., Davidson, C.M. & Thomas, R.P. (1995). Single and sequential extraction schemes for tracę metal speciation in soil and sediment, Techniąues and Instruinentation in Analytical Chemistry, 17, pp. 505-523.
  37. Vassilev, S., Baxter, D., Andersen, L. & Vassileva, C. (2013a). An overview of the composition and application of biomass ash. Part 1.Phase–mineral and chemical composition and classification. Fuel, 105, pp. 40–76.
  38. Vassilev, S., Baxter, D., Andersen, L. & Vassileva, C. (2013b). An overview of the composition and application of biomass ash. Part 2. Potential utilisation, technological and ecological advantages and challenges. Fuel, 105, pp. 19-39.
  39. Wojtkowska, M. & Bogacki, J. (2012). Use of Speciation Analysis for Monitoring Heavy Metals in the Bottom Sediments of the Utrata River‎, Environmental Protection, 34, 4, pp. 43-46.
  40. Woodard, C. (2006). Industrial Waste Treatment Handbook. Second Edition, Elselvier, USA.
  41. Wzorek, Z. (2008). Recovery of phosphorous compounds from thermally processed waste and their application as a substitute for natural phosphorous raw materials. Kraków, Publishing House of the Cracow University of Technology.
Go to article

Authors and Affiliations

Paweł Falaciński
1
ORCID: ORCID
Małgorzata Wojtkowska
1

  1. Warsaw University of Technology, Faculty of Building Services, Hydro and Environmental Engineering, Warsaw
Download PDF Download RIS Download Bibtex

Abstract

The objective of this work was investigation of the growth dynamics of proteolytic bacteria and the enzymatic activity in soil for the cultivation of maize (Zea mays L.), as well as the maize yield under application of some selected organic fertilizers. Intensity and the direction of the developed changes in the soil depended on the type of applied organic fertilizer, the size of its dose introduced into the soil and on the developmental phase of the grown plant (maize). On the basis of obtained results it was found that all tested organic substances stimulated the activity of proteases. Yields ofmaize as raw material for silages obtained from soil fertilized with sewage sludge were similar to those obtained after the application of pig slurry and they exceeded maize yields harvested from other ferti I ization objects.
Go to article

Authors and Affiliations

Alicja Niewiadomska
Hanna Sulewska
Agnieszka Wolna-Maruwka
Justyna Klama
Download PDF Download RIS Download Bibtex

Abstract

Previous studies indicated that particle size distribution affects the composition of keratinolytic and keratinophilic fungi in sewage sludge. The present study was to determine the composition of these fungi in sludge particle size fractions (> I, 1-0.5, 0.5--0.25, 0.25--0.125, 0.125-0.063, O 063--0.032 and < 0.032 mm) in a model experiment. I n the original sludge sample and its fractions, the composition of keratinolytic and kcratinophilic fungi was determined by using the hair baiting method. The composition of actidioneresistant fungi was also determined by using the dilution method and the Wiegand medium supplemented with chloramphenicol ( I 00 mg/dm') and actidione (500 mg/dm3). The number of keratinolytic and keratinophilic fungi isolated by the hair baiting method was lower in fractions than in the original sludge sample. In contrast, fungal quantities obtained by the dilution method were higher in fractions than in the original sludge sample. Qualitative differences were also observed. The conclusion was that nutrient factors associated with sludge particle size fractions, chietly total sulfur content and C:S ratio, affected the composition of keratinolytic and keratinophilic fungi in the sludge more than the fungal propagule quantities (inocula).
Go to article

Authors and Affiliations

Krzysztof Ulfig
Grażyna Plaza
Maciej Terakowski
Download PDF Download RIS Download Bibtex

Abstract

The aim of the investigation was to determine the impact of the presence of Zn in concentrations of sludges applied in agriculture (exceeding concentrations determined in sludges drained from the treatment plant) 011 the disappearance of PAHs in sewage sludge stored under aerobic conditions. The studies were carried out using dewatered and biochemically stabilized sludges. The changes in the concentration of PAHs were studied in four series: in sludge samples taken after filter press, in sludge with the addition of a standard PAH mixture. in sludge with Zn added, in sludge with the addition of both the standard PAH mixture and Zn. The standard PAH mixture used in the studies contained 16 compounds in benzene - dichloromethane (I: ł) solution with a concentration of 32000 ug/cm' of 16 PAHs. Zn was added to the sludge samples as a solution of chloride zrnc. the final amount was below 2500 mg Zn/kg d.m. (taking into consideration the initial concentrations) The sludge samples were incubated for 90 days at 20°C with limitless access of oxygen. The determination of PAHs in sludge samples was done in duplicates at the beginning of the experiment (the initial concentration) and then six times at I 5-day intervals (after 15. 30. 45. 60. 75 and 90 days). A gas chromatography-mass spectrometry (GC-MS) was used to qualify and quantify the PAHs. I 6 PAI-ls listed by EPA were identified
Go to article

Authors and Affiliations

Maria Włodarczyk-Makuła
Marta Janosz-Rajczyk
Download PDF Download RIS Download Bibtex

Abstract

The research covered two lakes: Karczemne and Domowe Małe, which served as receivers for rainwater and municipal or industrial sewage. The sediment cores were obtained using a Kajak tube sampler. Analyses of HM, PAH and PCB were done by the AAS, ICP-AES and GC MS methods. OM, SiO2, TH, Ca, Mg, CO2, Fe, Al, Mn, TN and TP were measured. The research showed that the sediments of Lake Karczemne, into which the untreated municipal sewage was discharged, are characterized by a high content of P. It was found that the sediments accumulate toxins, OM and pollutants characteristic for various industries. Karczemne Lake which collected municipal and industrial wastewater, contained a high content of Pb, Cu and PAH in the sediments, and Domowe Małe Lake, receiving stormwater, contained high concentrations of PAH. Research has shown that one of the most important tools for selecting an appropriate method of lake restoration is the analysis of the spatial distribution of pollutants in the bottom sediments. Thanks to such an analysis of the composition of the bottom sediments and the correlation between the components of the sediments and their sorption properties, the restoration of the Karczemne Lake using the Ripl method was planned and the possibility of restoration of the Domowe Małe Lake in this way was eliminated.
Go to article

Bibliography

  1. Algül, F. & Beyhan, M. (2020). Concentrations and sources of heavy metals in shallow sediments in Lake Bafa, Turkey. Scientific Reports, 10, 11728. DOI:10.1038/s41598-020-68833-2.
  2. Alves, C., Gonçalves, C., Evtyugina, M., Pio, C., Mirante, F. & Puxbaum, H. (2010). Particulate organic compounds emitted form experimental wildland fires in a Mediterranean ecosystem. Atmospheric Environment, 44, 23, pp. 2750-2759. DOI:10.1016/j.atmosenv.2010.04.029.
  3. Augustyniak, R., Grochowska, J.K., Łopata, M., Parszuto, K., Tandyrak, R. & Tunowski, J. (2019). Sorption properties of the bottom sediment of a lake restored by phosphorus inactivation method15 years after the termination of the lake restoration procedures. Water, 11, 10, 1-20. DOI:10.3390/w11102175.
  4. Augustyniak, R., Neugebauer, M., Kowalska, J., Szymański, D., Wiśniewski, G., Filipkowska, Z., Grochowska, J., Łopata, M., Parszuto, K. & Tandyrak, R. (2015). Bottom deposits of stratified, seepage, urban lake (on the example of Tyrsko Lake, Poland) as a factor potentially shaping lake water quality. Journal of Ecological Engineering, 18, 5, pp. 55-62.
  5. Barbusiński, K. & Nocoń, W. (2011). Heavy metal compound content in Kłodnica bottom sediments. Environmental Protection, 33, 1, pp. 13 – 17. (in Polish)
  6. Bartoli, G., Papa, S., Sagnella, E. & Fioretto, A. (2012). Heavy metal content in sediments along the Calore river: Relationships with physical–chemical characteristics. Journal of Environmental Management, 95, pp. 9-14. DOI:10.1016/j.jenvman.2011.02.013.
  7. Bing, H.J., Wu, Y.H., Sunz, B. & Yao, S.C. (2011). Historical trends of heavy metal contamination and their sources in lacustrine sediment from Xijiu Lake, Taihu Lake Catchment, China. Journal of Environmental Sciences, 23, 10, pp. 1671-1678. DOI:10.1016/s1001-0742(10)60593-1.
  8. Birch, G. & Taylor, S. (1999). Source of heavy metals in sediments of the Port Jackson estuary, Australia. Science of The Total Environment, 227, (2–3), pp. 123-138.
  9. Bocca, B., Alimonti, A., Petrucci, F., Violante, N., Sancesario, G. & Forte, G. (2004). Quantification of trace elements by sector field inductively coupled plasma spectrometry in urine, serum, blood and cerebrospinal fluid of patients with Parkinson’s disease. Spectrochimica Acta, 59, 4, pp. 559–566. DOI:10.1016/j.sab.2004.02.007.
  10. Bojakowska, I. & Sokołowska, G. (1996). Heavy metals in lake sediments of the Kashubian Lake District. Geological Review, 44, 9, pp. 920 – 923. (in Polish)
  11. Bojakowska, I., Sztuczyńska, A. & Grabiec-Raczak, E. (2012). Monitoring studies of lake sediments in Poland: polycyclic aromatic hydrocarbons. Bulletin of the Polish Geological Institute, 450, pp. 17-26. (in Polish)
  12. Brzozowska, R. & Gawrońska, H. (2009). The influence of a long-term artificial aeration on the nitrogen compounds exchange between bottom sediments and water in Lake Długie. Oceanological and Hydrobiological Studies, 38, 1, pp. 113-119.
  13. Cappacioni, B., Martini, M. & Mangani, F. (1995). Light hydrocarbons in hydrothermal and magmatic fumaroles: hints of catalytic and thermal reactions. Bulletin of Volconalogy, 56, 8, pp. 593-600.
  14. Chen, M., Ding, S., Zhang, L., Li, Y., Sun, Q. & Zhang, Ch. (2017). An investigation of the effects of elevated phosphorus in water on the release of heavy metals in sediments at a high resolution. Science of The Total Environment, 575, pp. 330-337. DOI:10.1016/j.scitotenv.2016.10.063.
  15. Dhanakumar, S., Solaraj, G. & Mohanraj, R. (2015). Heavy metal partitioning in sediments and bioaccumulation in commercial fish species of three major reservoirs of river Cauvery delta region, India. Ecotoxicology and Environmental Safety, 113, pp. 145-151. DOI:10.1016/j.ecoenv.2014.11.032.
  16. EPA (2001). Parameters of Water Quality. Interpretation and Standards. Environmental Protection Agency, Wexford.
  17. Fu, J., Zhao, Ch., Luo, Y., Liu, Ch., Kyzas, G.Z., Luo, Y., Zhao, D., An, S. & Zhu, H. (2014). Heavy metals in surface sediments of the Jialu River, China: Their relations to environmental factors. Journal of Hazardous Materials, 270, pp. 102-109. DOI:10.1016/j.jhazmat.2014.01.044.
  18. Gabarrón, M., Faz, A., Martínez-Martínez, S., Zornoza, R. & Acosta, J.A. (2017). Assessment of metals behaviour in industrial soil using sequential extraction, multivariable analysis and a geostatistical approach. Journal of Geochemical Exploration, 172, pp. 174-183. DOI:10.1016/j.gexplo.2016.10.015.
  19. Grochowska, J., Augustyniak, R., Łopata, M. & Tandyrak, R. (2020). Is it possible to restore a heavily polluted, shallow, urban lake? Applied Science, 10, 11, pp. 3698. DOI:10.3390/app10113698.
  20. Grochowska, J., Augustyniak, R., Łopata, M., Parszuto, K., Tandyrak, R. & Płachta, A. (2019). From saprotrophic to clear water status: the restoration path of a degraded urban lake. Water, Air & Soil Pollution, 230, pp. 1-14. DOI:10.1007/s11270-019-4138-5.
  21. Grochowska, J., Tandyrak, R. & Wiśniewski, G. (2014). Long-term hydrochemical changes in a lake after the application of several protection measures in the catchment. Polish Journal of Natural Sciences, 29, 3, pp. 251 - 263.
  22. Håkanson, L. (1980). An ecological risk index for aquatic pollution control. A sedimentological approach. Water Research, 14, pp. 975-1001.
  23. Håkanson, L. (2004). Internal loading: A new solution to an old problem in aquatic sciences. Lake and Reservoir and Management, 9, 1, pp. 3-23. DOI:10.1111/j. 1440-1770.2004.00230.x.
  24. Hermanowicz, W., Dożańska, W., Dojlido, J., Koziorowski, B. & Zerbe, J. (1999). Physico - chemical study of water and wastewater. Ed. Arkady, Warsaw, Poland, 1999. (in Polish)
  25. Jansson, M. (1987). Anaerobic dissolution of iron-phosphorus complex in sediment due to the activity of nitrate-reducing bacteria. Microbial Ecology, 14, pp. 81-89.
  26. Jeremiason, J.D., Eisenreich, S.J. & Peterson, M.J. (2011). Accumulation and recycling of PCBs and PAHs in artificially eutrophied lake 227. Canadian Journal of Fisheries and Aquatic Sciences, 56, 4, pp. 650-660. DOI:10.1139/cjfas-56-4-650.
  27. Jeremiason, J.D., Eisenreich, S.J., Peterson, M.J., Beaty, K.G., Hecky, R. & Elser, J.J. (1999). Biogeochemical cycling of PCBs in lakes of variable trophic status: A paired-lake experiment. Limnology and Oceanography, 44, 3, 2, pp. 889-902. DOI:10.4319/lo.1999.44.3.
  28. Joniak, T., Jakubowska, N. & Szeląg-Wasilewska, E. (2013). Degradation of the recreational functions of urban lake: A preliminary evaluation of water turbidity and light availability (Strzeszyńskie Lake, Western Poland). Polish Journal of Natural Sciences, 28, pp. 43–51.
  29. Juśkiewicz, W., Marszelewski, W. & Tylmann, W. (2015). Differentiation of the concentration of heavy metals and persistent organic pollutants in lake sediments depending on the catchment management (Lake Gopło case study). Bulletin of Geography. Physical Geography Series, 8, 71-80. DOI:10.1515/bgeo-2015-0006.
  30. Kaca, E. (2003). Measurements of water flow volume and mass of substance contained in it, and its uncertainty on the example of fish ponds. Water-Environment-Rural Areas, 13, 41, pp. 31-57. (in Polish)
  31. Kang, X., Song, J., Yuan, H., Duan, L., Li, X., Li, N., Liang, X. & Qu, B. (2017). Speciation of heavy metals in different grain sizes of Jiaozhou Bay sediments: bioavailability, ecological risk assessment and source analysis on a centennial timescale. Ecotoxicology and Environmental Safety, 143, pp. 296-306. DOI:10.1016/j.ecoenv.2017.05.036.
  32. Katsoyiannis, A., Terzi, E. & Cai, Q.Y. (2007). On the use of PAH molecular diagnostic ratios in sewage sludge for the understanding of the PAH sources. Is this use appropriate? Chemosphere, 69, pp. 1337-1339. DOI:10.1016/j.chemosphere.2007.05.084.
  33. Kishe, M.A. & Machiwa, J.F. (2003). Distribution of heavy metals in sediments of Mwanza Gulf of Lake Victoria, Tanzania. Environment International, 28, 7, pp. 619-625. DOI:10.1016/S0160-4120(02)00099-5.
  34. Kondracki, J.A. (2011). Regional Geography of Poland. Ed. PWN, Warsaw, Poland. (in Polish)
  35. Kowalczewska-Madura, K., Dondajewska, R., Gołdyn, R., Kozak, A. & Messyasz, B. (2018). Internal phosphorus loading from the bottom sediments of a dimictic lake during its sustainable restoration. Water, Air & Soil Pollution, 229, 8, pp. 280. DOI:10.1007/s11270-018-3937-4.
  36. Kowalczewska-Madura, K., Gołdyn, R. & Dondajewska, R. (2011). Phosphorus release from the bottom sediments of Lake Rusałka (Poznań, Poland). Oceanological and Hydrobiological Studies, 38, 4, pp. 135-144. DOI:10.2478/VI00009-010-0046-0.
  37. LAWA – Länder-Arbeitsgemeinschaft Wasser. Beurteilung der Wasserbeschaffenheit von Fließgewässern in der Bundesrepublik Deutschland – chemische Gewässergüteklassifi kation. Zielvorgaben zum Schutz oberirdischer Binnengewässer, Berlin, Germany, Band 2, 10, pp. 1–26.
  38. Lidell, M., Bremle, G., Broberg, O. & Larsson, P. (2001). Monitoring of persistent organic pollutants (POPs): examples from Lake Väner, Sweden. Ambio 30, 8, pp. 545-551. DOI:10.1579/0044-7447-30.8.545.
  39. Liu, B., Xu, H., Lan, J., Sheng, E., Che, S. & Zhou, X. (2014). Biogenic silica contents of Lake Quinghai sediments and its environmental significance. Frontiers of Earth Science, 8, 4, pp. 573-581. DOI:10.1007/s11707-014-0440-0.
  40. Liu, D., Yuan, P., Tian, Q., Liu, H., Deng, L., Song, Y., Zhou, J., Losic, D., Zhou, J., Song, H., Guo, H. & Fan, W. (2019). Lake sedimentary biogenic silica from diatoms constitutes a significant global sink for aluminium. Nature Communications, 10, pp. 4829. DOI:10.1038/s41467-019-12828-9.
  41. Łopata, M. (2010). Water-legal survey for the introduction of substances inhibiting the growth of algae to the waters of Domowe Duże and Domowe Małe lakes in Szczytno in connection with the planned reclamation of the lakes using the phosphorus inactivation method. Typescript. (in Polish)
  42. Mamindy-Pajany, Y., Hamer, B., Romeo, M., Geret, F., Galgani, F., Durmisi, E., Hurel, Ch. & Marmier, N. (2011). The toxicity of composed sediments from Mediterranean ports evaluated by several bioassays. Chemosphere, 82, 3, pp. 362-369. DPO:10.1016/j.chemosphere.2010.10.005.
  43. Migaszewski, Z.M. & Gałuszka, A. (2003). Outline of environmental geochemistry. Publishing of the Świętokrzyska Academy, Kielce, Poland.(in Polish)
  44. Nasr, S.M., Okbah, M.A. & Kasem, S.M. (2006). Environmental assessment of heavy metal pollution in bottom sediments of Aden Port, Yemen. International Journal of Oceans and Oceanography, 1, 1, pp. 99-109.
  45. Ordinance of the Ministry of the Environment of 1 September 2016 on the method of conducting an assessment of the soil surface pollution. Journal of Laws of 2016, item 1395. (in Polish)
  46. Ordinance of the Ministry of the Environment of 11 May 2015 on the recovery of waste outside installations and equipment. Journal of Laws of 2015, item 796. (in Polish)
  47. Piaścik, H. (1996). Geological and geomorphological conditions of the Masurian Lake District and the Sępopolska Plain. Problem Journals of the Progress of Agricultural Sciences, 431, pp. 31-45. (in Polish)
  48. Piasecki, D. (1960). Geological and morphological sketch of the Radunia river basin. Annals of the Polish Geological Society, XXIX, 4, pp. 385-394. (in Polish)
  49. Planter, M., Jędrychowska, G. & Łaźniewski, J. (2005). Assessment of the purity of the Bartąg, Domowe Duże, Domowe Małe and Ukiel lakes according to the research from 2004. VIEP Olsztyn, 30, 2, pp. 1-5. (in Polish)
  50. Pohl, A., Kostecki, M., Jureczko, I., Czaplicka, M. & Łozowski, B. (2018). Polycyclic aromatic hydrocarbons in water and bottom sediments of a shallow, lowland dammed reservoir (on the example of reservoir Blachownia, South Poland). Archives of Environment Protection, 44, 1, pp. 10-23. DOI:10.24425/118177.
  51. Prosowicz, D. (2008). Metals in bottom sediments of Wigry Lake. Geologia, 34, pp. 85–108. (in Polish)
  52. Ripl, W. (1976a). Biochemical oxidation of polluted lake sediment with nitrate. A new restoration method. Ambio, 5, pp. 132–135.
  53. Ripl, W. (l976b). Prozeßsteuerung in geschädigten See-Ökosystemen. Vierteljahresschrift der Naturforschenden Gesell-schaft Zürich, 121, pp. 301–308.
  54. Roden, E.& Emonds, J. (1997). Phosphate mobilization in iron-rich anaerobic sediments: microbial Fe(III) oxide reduction versus iron-sulfide formation. Archive fur Hydrobiologie, 139, 3, pp. 347-378. DOI:10.1127/archiv-hydrobiol/139/1997/347.
  55. Sanders, G., Hamilton-Taylor, J. & Jones, K.C. (1996). PCB and PAH dynamics in a small rural lake. Environmental Science and Technology, 30, 10, pp. 2958-2966. DOI:10.10.21/es9509240.
  56. Sojka, M., Jaskuła, J. & Siepak, M. (2018). Heavy metals in bottom sediments of reservoirs in the lowland area of Western Poland: concentrations, distribution, sources and ecological risk. Water, 11, pp. 56. DOI:10.3390/w11010056.
  57. Stogiannidis, E. & Laane, R. (2015). Source characterization of polycyclic aromatic hydrocarbons by using their molecular indices: an overview of possibilities. In: Whitacre, D.M. (ed.) Reviews of environmental contamination and toxicology. Springer International Publishing, Switzerland, 234, pp. 49-133.
  58. Tibco Software Inc. STATISTICA version 13.0 2018.
  59. Waisberg, M., Joseph, P., Hale, B. & Beyersmann, D. (2003). Molecular and cellular mechanisms of cadmium carcinogenesis. Toxicology, 192, (2-3), pp. 95–117. DOI:10.1016/s0300-483x(03)00305-6.
  60. Wakida, F.T., Lara-Ruiz, D., Temores-Pen, J., Rodriguez-Ventura, J.G., Diaz, C. & Garcia-Flores, E. (2008). Heavy metals in sediments of the Tecate River, Mexico. Environmental Geology, 54, 3, pp. 637-642. DOI:10.1007/s00254-007-0831-6.
  61. Wang, X., Zhang, L., Zhao, Z. & Cai, Y. (2018). Heavy metal pollution in reservoir in the hilly area of southern China: Distribution, source apportionment and health risk assessment. Science of the Total Environment, 634, pp. 158-169. DOI:10.1016/j.scitotenv.2018.03.340.
  62. Wilson, D.C. (2018). Potential urban runoff impacts and contaminant distributions in shoreline and reservoir environments of Lake Havasu, southwestern United States. Science of the Total Environment, 621, pp. 95-107. DOI:10.1016/j.scitotenv.2017.11.223.
  63. Wróbel, P. (2012). Elaboration of bathymetry and morphometric chart of the Lake Domowe Małe. Typescript. (in Polish)
  64. Yunker, M.B., Macdonald, R.W., Vingarzan, R., Mitchell, R.H., Goyette, D. & Sylvestre, S. (2002). PAH in the Fraser River basin: a critical appraisal of PAH ratios as indicator of PAH source and composition. Organic Geochemistry, 33, pp. 489-515. DOI:10.1016/s0146-6380(02)00002.
  65. Zamparas, M. & Zacharias, I. (2014). Restoration of eutrophic freshwater by managing internal nutrient loads. Science of the Total Environment, 496, pp. 551-562. DOI:10.1016/j.scitotenv.2014.07.076.
Go to article

Authors and Affiliations

Jolanta Katarzyna Grochowska
1
ORCID: ORCID
Renata Tandyrak
1
Renata Augustyniak
1
ORCID: ORCID
Michał Łopata
1
Dariusz Popielarczyk
1
ORCID: ORCID
Tomasz Templin
1
ORCID: ORCID

  1. University Warmia and Mazury in Olsztyn, Poland
Download PDF Download RIS Download Bibtex

Abstract

To test the potential harmfulness of soils fertilized with sludge-based products to plant organisms, a biotest method using the physiological/biochemical reaction of the organisms to assess their toxicity was chosen. This paper presents the results of a preliminary ecotoxicological study of different products: a sludge-based fertilizer, a plant growth promoter, and a reclamation blend. The study was conducted using Sinapis alba L., a plant used in agriculture for intercropping and recommended for toxicological testing. Toxicity tests were performed in a gradient of concentrations of the indicated products (2.5%, 5%, and 10%). For comparison purposes, a trial containing a commercial fertilizer was used alongside the control soil (without additives). The fertilizer and the crop support agent were of low toxicity, but data analysis indicated toxicity of the so-called reclamation blend, which contained heavy metals among other things. The test products showed an increase in toxicity with the increasing dose used. This research represents an important step in assessing the usefulness of products created from sewage sludge and may help overcome the „psychological barrier” that prevents potential investors from investing capital that would allow production to spread.
Go to article

Bibliography

  1. Borgulat, J. (2020). Zróżnicowanie zawartości metali ciężkich i wielopierścieniowych węglowodorów aromatycznych (WWA) w igłach Picea abies oraz Abies alba w Beskidzie Śląskim i Żywieckim. [Unpublished doctoral dissertation]. University of Silesia
  2. Borgulat, J., Mętrak, M., Staszewski, T., Wiłkomirski, B., Suska-Malawska, M. (2018). Heavy Metals Accumulation in Soil and Plants of Polish Peat Bogs. Polish Journal of Environmental Studies, 27(2). DOI: 10.15244/pjoes/75823
  3. Breda, C.C., Bortolanza, M., Renan, S., Tavantic, F.R., Viana, D., Freddia, O., Piedade, A.R., Mahle, D.,Traballi, R.C., Guerrinig, I. (2020). Successive sewage sludge fertilization: Recycling for sustainable agriculture. Waste Management, 109, pp. 38-50. DOI:10.1016/j.wasman.2020.04.045
  4. Ciesielczuk, T., Rosik-Dulewska, C., Poluszyńska, J., Miłek, D., Szewczyk, A., & Sławińska, I. (2018). Acute toxicity of experimental fertilizers made of spent coffee grounds. Waste Biomass Valori, 9(11), pp. 2157-2164. DOI:10.1007/s12649-017-9980-3
  5. Food and Agriculture Organization of United Nations: Worlds Fertilizer trends and Outlook to 2022. FAO 2019.
  6. Grobelak, A., Stępień, W., & Kacprzak, M. (2016). Sewage sludge as a component of fertilizers and soil substitutes. Inż. Ekol. (in Polish). DOI: 10.12912/23920629/63289
  7. GUS, 2019. Ochrona Środowiska. (http://stat.gov.pl, 10.11.2020)
  8. Harasimowicz-Hermann, G., Hermann J. (2006). The function of catch crops in the protection of mineral resources and soil organic matter. Zesz. Probl. Post. Nauk Rol., I(512), pp. 147–155. (in Polish)
  9. Hase, T., Kawamura, K. (2012). Germination test on Komatsuna (Brassica rapa var. peruviridis) seed using water extract from compost for evaluating compost maturity: evaluating criteria for germination and effects of cultivars on germination rate. J. Mater. Cycles Waste Manage., 14(4), pp. 334–340. DOI:10.1007/s10163-012-0073-x
  10. Jakubus, M. (2012). Evaluation of compost by selected chemical and biological methods. Fresen. Environ. Bull., 21(11a), pp. 3464–3472.
  11. Journal of Laws. 2016 item 1395. Regulation of the Minister of the Environment of 1 September 2016 on the manner of conducting the assessment of pollution of the earth surface.
  12. Kaszycki, P., Głodniok, M., Petryszak, P (2021), Towards a bio-based circular economy in organic waste management and wastewater treatment – the Polish perspective. N Biotechnol, 61, pp. 80–89. DOI:10.1016/j.nbt.2020.11.005
  13. Ko, H., Kim, K., Kim, H., Kim, Ch., & Umeda, M. (2008). Evaluation of compost parameters and heavy metals contents in composts made from Animals mature. Waste. Manage., 28, pp. 813–820. DOI: 10.1016/j.wasman.2007.05.010
  14. Krzyżak, J., Pogrzeba, M., Rusinowski, S., Clifton-Brown, J., McCALMONT, J. P., Kiesel, A., & Mos, M. (2017). Heavy metal uptake by novel Miscanthus seed-based hybrids cultivated in heavy metal contaminated soil. CEER, 26(3), pp. 121–132. DOI: 10.1515/ceer-2017-0040
  15. Miaomiao, H., Wenhong, L., Xinqiang, L., Donglei, W., & Guangming, T. (2009). Effect of composting process on phytotoxicity and speciation of copper, zinc and lead in sewage sludge and swine manure. Waste Manage., 29, pp. 590–597. DOI:10.1016/j.wasman.2008.07.005
  16. Obidoska, G., Hadam, A. (2008). Phytotoxicity of composts produced from various urban wastes. Ann. Warsaw Univ. Life Sci. – SGGW, Horticult. Landsc. Architect., 29, pp. 65–70.
  17. OECD/ OCDE 208 ¬¬– Guidelines for the testing of chemicals. Terrestrial Plant Test: Seedling Emergence and Seedling Growth Test.
  18. PN-EN ISO 11269-1:2013-06 Soil quality. Determination of the effect of pollutants on soil flora - Method for measuring root growth inhibition. PN-EN ISO 11269-2:2013-06 Soil quality. Determination of the effect of pollutants on soil flora - Effect of chemical compounds on the emergence and growth of higher plants.
  19. Pogrzeba, M., Rusinowski, S., & Krzyżak, J. (2018). Macroelements and heavy metals content in energy crops cultivated on contaminated soil under different fertilization—case studies on autumn harvest. Environ Sci Pollut Res., 25(12), pp. 12096–12106. DOI: 10.1007/s11356-018-1490-8
  20. Preite, V., Sailer, C., Syllwasschy, L., Bray, S., Ahmadi, H., Krämer, U., & Yant, L. (2019). Convergent evolution in Arabidopsis halleri and Arabidopsis arenosa on calamine metalliferous soils. Philos. Trans. R. Soc. B, 374, pp. 20180243. DOI:10.1098/rstb.2018.0243
  21. Ren, Y., Lin, M., Liu, Q., Zhang, Z., Fei X., Xiao R., Lv X. (2021). Contamination assessment, health risk evaluation, and source identification of heavy metals in the soil-rice system of typical agricultural regions on the southeast coast of China. Environmental Science and Pollution Research, 28(10), 12870–12880. DOI:10.1007/s11356-020-11229-6
  22. Rosik-Dulewska, C., Głowala, K., Karwaczyńska, U., & Szydło, E (2006). The mobility of chosen pollutants from ash-sludge mixtures. Polish J. Environ. Stud., 15(6), pp. 895–904.
  23. Rosik-Dulewska, Cz., Karwaczyńska, U., & Głowala, K. (2007). Natural use of municipal sewage sludge and compost from municipal waste - fertilization value and environmental hazards. Zesz. Nauk. Wydz. Bud. i Inż. Środ., 23, pp. 137–153. (in Polish)
  24. Sarkheil, H., & Azimi, Y. (2020). Evaluation of Plant Roots Ability to Remove Lead and Zink Mining Drainage Contamination by Geoelectric Surveys. In NSG2020 3rd Conference on Geophysics for Mineral Exploration and Mining, 2020(1), pp. 1–4. European Association of Geoscientists & Engineers. DOI:10.3997/2214-4609.202020020
  25. Sawicka, B., Kotiuk, E. (2006). Evaluation of health safety of mustards in the obligatory norms. Acta Sci. Pol., Technol. Alim., 5(2), pp. 165–177.
  26. Skubała, K. (2011). Vascular Flora of Sites Contaminated with Heavy Metals on the Expample of Two Post-Industrial Spoil Heaps Connected with Manufacturing of Zinc and Lead Products in Upper Silesia. Archives of Environmental Protection, 37(1), pp. 57–74.
  27. Smol, M., Kulczycka, J., Lelek, Ł., Gorazda, K., & Wzorek, Z. (2020). Life Cycle Assessment (LCA) of the integrated technology for the phosphorus recovery from sewage sludge ash (SSA) and fertilizers production. Archives of Environmental Protection, 46(2). DOI: 10.24425/aep.2020.133473
  28. Tran, K. Q., Werle, S., Trinh, T. T., Magdziarz, A., Sobek, S., & Pogrzeba, M. (2020). Fuel characterization and thermal degradation kinetics of biomass from phytoremediation plants. Biomass and Bioenergy, 134, 105469. DOI:10.1016/j.biombioe.2020.105469
  29. Vimala, T., & Poonghuzhali, T. (2015). Estimation of pigments from seaweeds by using acetone and DMSO. IJSR, 4(10), pp. 1850–1854.
  30. Wójcik, M., Gonnelli, C., Selvi, F., Dresler, S., Rostański, A., & Vangronsveld, J. (2017). Metallophytes of serpentine and calamine soils–their unique ecophysiology and potential for phytoremediation. Adv. Bot. Res, 83, pp. 1–42. DOI:10.1016/bs.abr.2016.12.002
  31. Zawadzki, P., Głodniok, M. (2021), Environmental Safety Assessment of Fertilizer Products, Pol. J. Environ. Stud. 30(1):11–22. DOI:10.15244/pjoes/120519
  32. Zeynep, G. D. (2019). Role of EDDS and ZnO-nanoparticles in wheat exposed to TiO2Ag-nanoparticles. Archives of Environmental Protection, 45(4), pp. 78–83. DOI: 10.24425/aep.2019.130244
  33. Zhang, Z., Wu, X., Wu, Q., Huang, X., Zhang, J., Fang, H. (2020). Speciation and accumulation pattern of heavy metals from soil to rice at different growth stages in farmland of southwestern China. Environmental Science and Pollution Research, 27(28), 35675–35691. DOI:10.1007/s11356-020-09711-2
Go to article

Authors and Affiliations

Anna Borgulat
1
Aleksandra Zagórska
1
Marcin Głodniok
1

  1. Central Mining Institute, Department of Water Protection, Katowice, Poland

This page uses 'cookies'. Learn more