Search results

Filters

  • Journals
  • Authors
  • Keywords
  • Date
  • Type

Search results

Number of results: 38
items per page: 25 50 75
Sort by:
Download PDF Download RIS Download Bibtex

Abstract

In Mexico, one of the principal natural resources is oil, however, the activity related to it has generated hydrocarbon spills on agricultural soils. The aim of this study was to evaluate the biodegradability of diesel by means of indigenous bacteria isolated from agricultural soil contaminated with 68 900 mg kg -1 diesel. We examined indigenous bacterial strains in agricultural soils contaminated with diesel from Acatzingo, Puebla, Mexico. We performed a physicochemical soil characterization, and a bacterial population quantification favoring sporulated bacteria of the genera Bacillus and Paenibacillus taken from the study site. Six bacterial strains were isolated. The identification was made based on the 16S rRNA gene and API systems. The tolerance and biodegradation capacity in diesel were determined at 4 000 to 24 000 mg L -1 of diesel. Residual concentrations of diesel were determined by GC-FID. Soil contaminated with diesel alters the concentrations of organic matter, phosphorus and nitrogen. Analysis of soil samples showed heat resistant bacterial populations of 106 cfu g -1 dry soil. Six strains from soil pollution were identified – Pseudomonas stutzeri M1CH1, Bacillus pumilus M1CH1b, Bacillus cereus M1CH10, Bacillus subtilis M1CH15a, and Paenibacillus lautus strains M1CH19 and M1CH27. These bacteria showed different degradation behavior. Bacillus pumilus M1HC1b and Paenibacillus lautus M1CH27 use diesel oil as the sole carbon source. Bacillus pumilus degraded high concentrations of diesel (24 000 mg L -1), while for Paenibacillus lautus it became toxic and the degradation was less.
Go to article

Authors and Affiliations

Amparo Mauricio-Gutiérrez
1
Rocío Machorro-Velázquez
2
Teresita Jiménez-Salgado
3
Candelario Vázquez-Crúz
3
María Patricia Sánchez-Alonso
3
Armando Tapia-Hernández
3

  1. CONACYT – Instituto de Ciencias, Posgrado en Ciencias Ambientales, Benemérita Universidad Autónoma de Puebla, Mexico
  2. Facultad de Ciencias Biológicas, Benemérita Universidad Autónoma de Puebla, Mexico
  3. Centro de Investigación en Ciencias Microbiológicas, Instituto de Ciencias, Benemérita Universidad Autónoma de Puebla, Mexico
Download PDF Download RIS Download Bibtex

Abstract

This paper presents the content changes in the Chemical Oxygen Demand (COD) solubilised in hydrolisates obtained from thermally disintegrated municipal waste biofractions. A series of tests related to biowaste undergoing thermal treatment at the following temperatures: 55, 75, 95, 115, 135, 155 and 175°C were conducted for 0.5, 1 and 2 hours. The highest increase in COD solid fraction solubilisation (238%) was observed for the samples disintegrated at 175°C for 2 hours. The values of the reaction rate coefficient k20 = 0.6 d-1 and temperature coefficient θ = 1.023 were determined. Statistical analysis of the multiple regression (correlation coefficient R = 0.89) showed that the temperature has a greater impact on COD solid fraction solubilisation - determined β = 0.66. The multiple correlation coefficient for the treatment time was β = 0.61.

Go to article

Authors and Affiliations

Sylwia Myszograj
Download PDF Download RIS Download Bibtex

Abstract

The objective of the present study was to investigate the effects of Sn addition on the mechanical and corrosion properties of Mg-1Zn-1Zr-xSn (x = 1, 2, 3, 4, 5 wt.%) alloys prepared by powder-in-tube rolling (PTR) method. The PTR-treated Mg alloys reached 98.3% of theoretical density. The hardness of the alloy increased with Sn addition. Two main intermetallic phases, Mg2Sn and Zn2Zr3, were formed in the alloys. The Mg2Sn intermetallic particles were observed along the grain boundaries, while the Zn2Zr3 particles were distributed in the Mg matrix. The addition of 1 wt. % Sn caused the corrosion potential to shift toward a more positive value, and the resulting alloy exhibited low corrosion current density.

Go to article

Authors and Affiliations

A. Zakiyuddin
K. Lee
Download PDF Download RIS Download Bibtex

Abstract

The analysis of water self-purification process includes headstreams of rivers in the Upper Silesian agglomeration: the Bierawka, the Kłodnica, Bielszowicki creek and the Szotkówka. These are rivers characterized by small natural flows and a significant anthropogenic pol I utant load. Results of our own research on the self-purification rate were used. The attention was focused on biodegradable substances. The biodegradation rate coefficient k, and water assimilative capacity were determined. Within the same rivers, their particular parts differ in types of a riverbed and swift currents alternate with slow flows. In the case of Bielszowicki creek and the Szotkówka River impoundments were observed, which results in different self-purification conditions. In all investigated parts the rate of organic substance removal, characterized byk, coefficients, was usually much higher than the literature values for comparable rivers, which usually are below 2.0, rarely exceeding 3.0. The creek impoundments occurring in the watercourse beds do not always have a positive impact on the water quality. The role of the creek impoundments in the river self-purification process and their impact on water ecosystems require separate investigations.
Go to article

Authors and Affiliations

Rudolf Bujok
Download PDF Download RIS Download Bibtex

Abstract

Due to the observed increase in the amount of waste in landfills, there has been an increase in the demand for products made of biomaterials and the composition of biomaterials with petroleum-derived materials. The problem of waste disposal/management also applies to waste from the casting production process with the use of disposable casting moulds made with the use of organic binders (resins), as well as residues from the process of regeneration of moulding sands. A perspective solution is to add a biodegradable component to the moulding/core sand. The authors proposed the use of polycaprolactone (PCL), a polymer from the group of aliphatic polyesters, as an additive to a casting resin commonly used in practice. As part of this study, the effect of PCL addition on the (bio) degradation of dust obtained after the process of mechanical regeneration of moulding sands with organic binders was determined. The (bio) degradation process was studied in the environment reflecting the actual environmental conditions. As part of the article, dust samples before and after the duration of the (bio) degradation process were tested for weight loss by thermogravimetry (TG) and for losses on ignition (LOI).
Go to article

Bibliography

[1] Bastian, K.C., Alleman, J.E. (1996). Environmental bioassay evaluation of foundry waste residuals. Joint Transportation Research Program Technical Report Series, Purdue University, Purdue e-Pubs.
[2] Brenner, V. (2003). Biodegradace persistentních xenobiotik. Biodegradace. VI, 2003, 45-47.
[3] Sobków, D., Barton, J., Czaja, K., Sudoł, M. & Mazoń, B. (2014). Research on the resistance of materials to environmental factors. CHEMIK. 68(4), 347–354. (in Polish).
[4] Stachurek I. (2010). Biomedical systems of polyethylene oxide biodegradable in the aquatic environment. PhD thesis, Politechnika Krakowska. (in Polish).
[5] Eastman, J. (2000). Protein-based binder update: performance put to the test. Modern Casting. 90, 32-34.
[6] Kramářová, D., Brandštetr, J., Rusín, K. & Henzlová, P. (2003). Biogenic polymeric materials as binders for foundry molds and cores. Slévárenství. 60(2-3), 71-73. (in Czech).
[7] Grabowska, B., Holtzer, M., Dańko, R., Górny, M., Bobrowski, A. & Olejnik, E. (2013). New bioco binders containing biopolymers for foundry industry. Metalurgija. 52(1), 47-50.
[8] Grabowska, B., Szucki, M., Suchy, J.Sz., Eichholz, S., Hodor, K. (2013). Thermal degradation behavior of cellulose-based material for gating systems in iron casting production. Polimery. 58(1), 39-44.
[9] Major-Gabryś, K. (2016). Environmentally Friendly Foundry Moulding and Core Sands. Katowice-Gliwice, Archives of Foundry Engineering, ISBN 978-83-63605-24-7 (in Polish)
[10] Major-Gabryś, K. (2019). Environmentally Friendly Foundry Molding and Core Sands. Journal of Materials Engineering and Performance. 28(7), 3905-3911.
[11] Holtzer, M. (2001). Management of waste and by-products in foundries. Kraków: University Scientific and Didactic Publishers, AGH, Poland. (in Polish).
[12] Skrzyński, M., Dańko, R. & Czapla, P. (2014). Regeneration of used moulding sand with furfuryl resin on a laboratory stand. Archives of Foundry Engineering. 14(spec.4), 111-114. (in Polish).
[13] Dańko, R., Łucarz, M. & Dańko, J. (2014). Mechanical and mechanical-thermal regeneration of the used core sand from the cold-box process. Archives of Foundry Engineering. 14(spec.4), 21-24. (in Polish).
[14] Rui, T., Liu, J. (2010). Study of modified furan resin binder system for large steel castings. In Proceedings of 69th World Foundry Congress, 16 - 20 October 2010. Hangzhou, China, World Foundry Organization (pp. 996 – 999).
[15] Dańko, R., Holtzer, M., Dańko, J. (2015). Characteristics of dust from mechanical reclamation of moulding sand with furan cold-setting resins – impact on environment. In Proceedings of the 2015 WFO International Forum on Moulding Materials and Casting Technologies, 25 – 28 September 2015. Changsha, China. WFO Moulding Materials Commission, Foundry Institution of Chinese Mechanical Engineering Society, Productivity Center of Foundry Industry of China (38-46).
[16] Iwamoto, A. & Tokiwa, Y. (1994). Enzymatic degradation of plastics containing polycaprolactone. Polymer Degradation and Stability. 45(2), 205-213.
[17] Eastmond, G.C. (2000). Poly(ε-caprolactone) blends. Advances in Polymer Science. 149, 59-222.
[18] Gutowska, A., Michniewicz, M., Ciechańska, D. & Szalczyńska, M. (2013). Methods of testing the biodegradability of biomass materials. CHEMIK. 67(10), 945-954. (in Polish).
[19] Major-Gabryś, K., Hosadyna-Kondracka, M., Skrzyński, M., Pastirčák, R. (2020). The quality of reclaim from moulding sand with furfuryl resin and PCL additive. The abstract paper at XXVI international conference of Polish, Czech and Slovak founders: 7-9.09.2020 r. Baranów Sandomierski, Poland.
[20] Major-Gabryś, K., Hosadyna-Kondracka, M. & Stachurek, I. (2020). Determination of mass loss in samples of post-regeneration dust from moulding sands with and without PCL subjected to biodegradation processes in a water environment. Journal of Applied Materials Engineering. 60(4), 121-129.
Go to article

Authors and Affiliations

K. Major-Gabryś
1
ORCID: ORCID
I. Stachurek
2
ORCID: ORCID
M. Hosadyna-Kondracka
2
ORCID: ORCID

  1. AGH University of Science and Technology, Faculty of Foundry Engineering, Mickiewicza 30, 30-059 Cracow, Poland
  2. ŁUKASIEWICZ Research Network - Foundry Research Institute, Zakopianska 73, 30-418 Cracow, Poland
Download PDF Download RIS Download Bibtex

Abstract

Petroleum pollution is still one or crucial environmental problems. Bioaugmcntation is a popular technique used in soil remediation. The aim of soil inoculation is acceleration or decomposition processes or improving the degradation efficiency. Effectiveness of bioaugmentation processes depends on the number and activity of microorganisms adapted to pollutant degradation. Enhancement of microorganisms' activity can be reached by the use or plants. Roots or plants excrete organic substances that stimulate microorganisms' growth. Among different species or plants interesting arc papilionaceous plants because of their nitrogen fixation ability in symbiosis with bacteria. The effects or using papilionaceous plants (Trifolium pratense), multiplied autochthonous microorganisms and commercial biopreparation in aged-petroleumpolluted soil were studied. The samples of soil were taken from the refinery in Czechowice-Dziedzice (Poland) and classified as heavily degraded with a C/N-ratio or 100:0.7. Investigations were conducted for 14 weeks. Microbiological analysis included: total bacteria, fungi, Actinomycetes and Pscudonionas counts. Concentration or heavy fractions, TPH (total petroleum hydrocarbons) and PAHs (polycyclic aromatic hydrocarbons) were measured at the start and at the end of the experiment. Presence of pap il ionaceous plant (Trifolium pratensei enhanced the growth or microorganisms, nitrogen concentration and biodegradation processes (removal of 63% or TPH, 44% or heavy fractions, 9% or 4-6 aromatic PAHand 80% of 2-3 aromatic PAH) in polluted soil. An increasing number of Pseudomonas species was observed in samples in which pollution removal was more effective.
Go to article

Authors and Affiliations

Ewa Zabłocka-Godlewska
Wioletta Przystaś
Download PDF Download RIS Download Bibtex

Abstract

Biodegradation of organic matter by sulphate-reducing bacteria (SRB) isolated from soil from military testing ground and petroleum plants were investigated. The isolated microorganisms utilized low molecular weight compounds and participation of SRB in biodegradation of these compounds was similar in marine sediments and in soil (40-55%).
Go to article

Authors and Affiliations

Dorota Wolicka
Andrzej Borkowski
Download PDF Download RIS Download Bibtex

Abstract

In this study the effect of anionic surfactants on the morphology of activated sludge floes and biomass activity is quantitatively described. Three anionic surfactants: sodium dodecyl sulphate, sodium alkylbenzene sulphonate and sodium alkyltrioxyethylene sulphate were tested. The batch experiments were performed for a wide range of initial concentrations of anionics in wastewater from 2.5 to 2500 mgdm3. In spite of different chemical structure the action of all tested anionic surfactants resulted in the decrease of activated sludge floes dimensions at the similar level. It occurred that in the range of anionics concentrations, which are typical for domestic wastewater (2.5-25 mgdm3), they contributed to the decrease of mean projected area of floes by about 30%, whereas at the concentrations of 250 and 2500 mg-dm3 mean projected area decreased usually by 50-60%. Sodium alkylbenzene sulphonate exerted the strongest inhibition effect on dehydrogenase activity of activated sludge biomass. This effect coincided with the decreased degrees of removal for this surfactant and its biodegradation products, especially at its lower initial concentrations in wastewater.
Go to article

Authors and Affiliations

Ewa Liwarska--Bizukojc
Marcin Bizukojc
Download PDF Download RIS Download Bibtex

Abstract

In environmental matrices there are mixtures of parent drug and its metabolites. The majority of research is focused on the biological activity and toxic effect of diclofenac (DCF), there is little research on the biological activity of DCF metabolites and their mixtures. The study focused on the assessment of the biological impact of DCF, its metabolites 4’-hydroxydiclofenac (4’-OHDCF) and 5-hydroxydiclofenac (5-OHDCF) and their mixtures on E. coli strains. The biological effects of tested chemicals were evaluated using the following: E. coli K-12 cells viability assay, the inhibition of bacteria culture growth, ROS (reactive oxygene species) generation and glutathione (GSH) content estimation. Moreover, we examined the influence of the mixture of DCF with caffeic acid (CA) on E. coli cells viability. Our results showed the strongest impact of the mixtures of DCF with 4’-OHDCF and 5-OHDCF on E. coli SM biosensor strains in comparison to parent chemicals. Similar results were obtained in viability test, where we noticed the highest reduction in E. coli cell viability after bacteria incubation with the mixtures of DCF with 4’-OHDCF and 5-OHDCF. Similarly, these mixtures strongly inhibited the growth of E. coli culture. We also found synergistic effect of caffeic acid in combination with DCF on E. coli cells viability. After bacteria treatment with the mixture of DCF and its metabolites we also noted the strongest amount of ROS generation and GSH depletion in E. coli culture. It suggests that oxidative stress is the most important mechanism underlying the activity of DCF and its metabolites.

Go to article

Authors and Affiliations

Marzena Matejczyk
1
Piotr Ofman
2
Katarzyna Dąbrowska
3
Renata Świsłocka
1
Włodzimierz Lewandowski
1

  1. Bialystok University of Technology, Faculty of Civil Engineering and Environmental Sciences, Division of Chemistry, Biology and Biotechnology, Bialystok, Poland
  2. Bialystok University of Technology, Faculty of Environmental Engineering Technology and Systems, Bialystok University of Technology, Bialystok, Poland
  3. Department of Microbiology, Institute of Agricultural and Food Biotechnology, Warsaw, Poland
Download PDF Download RIS Download Bibtex

Abstract

The Fe-based alloy with manganese led to the appearance of new austenitic alloys, with the antiferromagnetic property pursued, resulting in compatibility with the magnetic field as that of magnetic resonance imaging. The corrosion resistance behavior of the biodegradable Fe-Mn-Si alloy was analyzed in a thermostatic chamber at 37±1°C for 24, 48 and 72 hours by immersing in Ringer solution. Also, the cast and laminated samples were subjected to electro-corrosion tests using a potentiostat equipment. Linear and cyclic potentiometry is presented for characterize the corrosion behavior of the experimental samples in electrolyte. Due to the interaction between the alloy and the liquid medium a change in the solution pH was observed. Structure analysis and chemical composition details of the surfaces were obtained using electron scanning microscopy (SEM) and X-ray energy dispersive spectroscopy (EDS).
Go to article

Authors and Affiliations

A.-M. Roman
1
ORCID: ORCID
R. Chelariu
1
ORCID: ORCID
R. Cimpoesu
1
ORCID: ORCID
I. Stirbu
1
ORCID: ORCID
I. Ionita
1
ORCID: ORCID
M.M. Cazacu
2
ORCID: ORCID
B.A. Prisecariu
3
ORCID: ORCID
N. Cimpoesu
3
ORCID: ORCID
P. Pietrusiewicz
4
ORCID: ORCID
A. Sodor
3
ORCID: ORCID

  1. Faculty of Materials Science and Engineering, “Gheorghe Asachi” Technical University of Iasi, Prof.dr.doc. D. Mangeron no. 41 Street, 700050 Iasi, Romania
  2. “Gheorghe Asachi” Technical University of Iasi, Department of Physics, 700050 Iasi, Romania
  3. “Grigore T. Popa” University of Medicine and Pharmacy of Iasi, 16 Univ. Street, 700115 Iasi, Romania
  4. Częstochowa University of Technology, Department of Physics , 42-200 Częstochowa, Poland
Download PDF Download RIS Download Bibtex

Abstract

Plastics have become indispensable in everyday life due to their properties. For this reason, the accumulation of polymer waste in the natural environment is becoming a serious global problem. The aim of the research was to isolate microorganisms capable of biodegrading plastics. The studies focused on the biodegradation of low-density polyethylene as the most common polymer. Seven and five bacterial strains were isolated from the landfill and compost, respectively. The morphological and biochemical characteristics of the isolates were determined. These isolates were able to survive in an environment where the only carbon source was LDPE, but no increase in biomass was obtained. However, analysis of the spectra obtained by the ATR-FTIR method showed the formation of chemical changes on the polymer surface. Bacterial biofilm formation was visualized by scanning electron microscopy. The toxicity of plastic biodegradation products in a liquid environment was tested and their safety for plants was confirmed. However, these biodegradation products have acute lethal toxicity for the Daphnia magna.
LDPE films were pre-treated with H 2O 2, HNO 3, or heat. The biodegradation of HNO 3-treated LDPE by isolated bacteria was the most significant. The weight loss was approximately 8%, and 6%, for landfill and compost-isolated bacterial strains, respectively.
Go to article

Authors and Affiliations

Elżbieta Szczyrba
1
ORCID: ORCID
Tetiana Pokynbroda
2
ORCID: ORCID
Nataliia Koretska
2
ORCID: ORCID
Agnieszka Gąszczak
1
ORCID: ORCID

  1. Instytut Inżynierii Chemicznej Polskiej Akademii Nauk, ul. Bałtycka 5, 44-100 Gliwice, Poland
  2. Department of Physical Chemistry of Fossil Fuels of the Institute of Physical-Organic Chemistry and Coal Chemistry named after L.M. Lytvynenko of the National Academy of Sciences of Ukraine, Naukova str, 79060, Lviv, Ukraine
Download PDF Download RIS Download Bibtex

Abstract

The large diversity of chemical substances present in air, water, or soil makes it necessary tostudy their mutual impact on the effectiveness of microbiological decomposition ofcontaminants. This publication presents the results of the studies aimed at evaluating the effect of two biogenic heavy metals - zinc and copper - on the phenol biodegradation by the Stenotrophomonas maltophilia KB2 strain. The tests were carried out for concentrations ofmetals significantly exceeding the legally permitted wastewater values: for zinc up to13.3 g·m -3, and copper up to 3.33 g·m -3. In the tested metal concentration range, phenol biodegradation by the S. maltophilia KB2 strain was not significantly influenced by theintroduced dose of zinc. While the presence of copper inhibited both biomass growth andsubstrate degradation. Kinetic data of metal and phenol mixtures were analyzed and very goodcorrelations were obtained for the proposed equations. An equation consistents with the Hanand Levenspiel model was proposed for the system S. maltophilia KB2-phenol-copper, whilean equation consistents with the Kai model for the system St. maltophilia KB2-phenol-zinc. The simultaneous presence of Zn and Cu ions in the culture resulted in a stronger inhibition ofphenol biodegradation.
Go to article

Authors and Affiliations

Agnieszka Gąszczak
1
ORCID: ORCID
Elżbieta Szczyrba
1
ORCID: ORCID
Anna Szczotka
1
ORCID: ORCID

  1. Polish Academy of Sciences, Institute of Chemical Engineering, Baltycka 5, 44-100 Gliwice, Poland
Download PDF Download RIS Download Bibtex

Abstract

Growing emission requirements are forcing the foundry industry to seek new, more environmentally friendly solutions. One of the

solutions may be the technologies of preparing moulding and core sands using organic biodegradable materials

as binders. However, not only environmental requirements grow but also those related to the technological properties

of moulding sand. Advancing automation and mechanization of the foundry industry brings new challenges related to the moulding sands.

Low elasticity may cause defects during assembly of cores or moulds by the manipulators.

The paper presents the study of flexibility in the room temperature according to new method and resistance to thermal deformation of selfhardening

moulding sands with furfuryl resin, containing biodegradable material PCL. The task of the new additive is to reduce the

moulding sands harmfulness to the environment and increase its flexibility in the room temperature. The impact of the additive and the

effect of the amount of binder on the properties of mentioned moulding sands were analysed. Studies have shown that the use of 5% of

PCL does not change the nature of the thermal deformation curve, improves the bending strength of tested moulding mixtures and

increases their flexibility at room temperature.

Go to article

Authors and Affiliations

A. Grabarczyk
K. Major-Gabryś
St.M. Dobosz
Download PDF Download RIS Download Bibtex

Abstract

The article shows the influence of environment requirements on changes in different foundry moulding sands technologies such as cold

box, self-hardening moulding sands and green sands. The aim of the article is to show the possibility of using the biodegradable materials

as binders (or parts of binders’ compositions) for foundry moulding and core sands. The authors concentrated on the possibility of

preparing new binders consisting of typical synthetic resins - commonly used in foundry practice - and biodegradable materials. According

to own research it is presumed that using biodegradable materials as a part of new binders’ compositions may cause not only lower toxicity

and better ability to reclaim, but may also accelerate the biodegradation rate of used binders. What’s more, using some kinds of

biodegradable materials may improve flexibility of moulding sands with polymeric binder. The conducted research was introductory and

took into account bending strength and thermal properties of furan moulding sands with biodegradable material (PCL). The research

proved that new biodegradable additive did not decrease the tested properties.

Go to article

Authors and Affiliations

St.M. Dobosz
A. Grabarczyk
K. Major-Gabryś
Download PDF Download RIS Download Bibtex

Abstract

The paper presents possibility of using biodegradable materials as parts of moulding sands’ binders based on commonly used in foundry

practice resins. The authors focus on thermal destruction of binding materials and thermal deformation of moulding sands with tested

materials. All the research is conducted for the biodegradable material and two typical resins separately. The point of the article is to show

if tested materials are compatible from thermal destruction and thermal deformation points of view. It was proved that tested materials

characterized with similar thermal destruction but thermal deformation of moulding sands with those binders was different.

Go to article

Authors and Affiliations

St.M. Dobosz
J. Jakubski
K. Major-Gabryś
D. Drożyński
Download PDF Download RIS Download Bibtex

Abstract

The paper presents the impact of biodegradable material - polycaprolactone (PCL) on selected properties of moulding sands. A self-hardening moulding sands with phenol-furfuryl resin, which is widely used in foundry practice, and an environmentally friendly self-hardening moulding sand with hydrated sodium silicate where chosen for testing. The purpose of the new additive in the case of synthetic resin moulding sands is to reduce their harmfulness to the environment and to increase their “elasticity” at ambient temperature. In the case of moulding sands with environmentally friendly hydrated sodium silicate binder, the task of the new additive is to increase the elasticity of the tested samples while preserving their ecological character. Studies have shown that the use of 5% PCL in moulding sand increases their flexibility at ambient temperature, both with organic and inorganic binders. The influence of the new additive on the deformation of the moulding sands at elevated temperatures has also been demonstrated.
Go to article

Authors and Affiliations

A. Grabarczyk
S.M. Dobosz
K. Major-Gabryś
Download PDF Download RIS Download Bibtex

Abstract

TCE artificially contaminated soil was cleaned under anaerobic, reductive conditions. A laboratory scale treatability studies were carried out to determine optimal physico-chcmical and microbiological parameters for biorcmcdiation process. Upon treatability studies results a sewage sludge mixture was chosen as a microorganism's source. The chlorinated solvents contaminated soil bioreactor (CSCS bioreactor) was designed and built. It consists of a 6 m3 reactor vessel, a gas recirculation system, a leachate recirculation system and a data acquisition system. The bioreactor vessel was designed as a continuous gas flow packed bed reactor. During 210 days 4 Mg of soil containing approximately 350 mg TCE/kg of soil has been completely remediated under anaerobic conditions. The obtained results indicate that the stepwise dechlorination of TCE to ETH occurs in the bioreactor. Increasing amounts of chloride in the leachate were correlated with dechlorination.
Go to article

Authors and Affiliations

Adam Worsztynowicz
Dorota Rzychoń
Tomasz Siobowicz
Sebastian lwaszenko
Grażyna Płaza
Krzysztof Ulfig
Download PDF Download RIS Download Bibtex

Abstract

Fungus Fnsarium solani, able to degrade methyl isobutyl ketone was isolated from the bed ofbiofilter cleaning exhausting gases from the cable plant "Załom" near Szczecin. This substance was used as the only source of carbon and energy. Confirmation and kinetic tests were performed in 25 cm- scrubbers filed with mineral medium which was inoculated with the fungus. Fusorium solani degraded MIBK at the rate up to 60 g·m3·h·1 and pollution loading up to 200 gm+h'. Degree of elimination ranged from 40 to 80% and decreased when culture pollution loading increased.
Go to article

Authors and Affiliations

Krystyna Przybulewska
Andrzej N. Wieczorek
Download PDF Download RIS Download Bibtex

Abstract

Exploited lubricants are dangerous contaminants because of their toxicity and low biodegradability. In this study, microbial culture active in exploited lubricant oil Mobil I was isolated and inoculated to sandy soil containing 0.5 g of contaminant per 100 g of dry soil. Microorganisms were used as free cells and immobilizate on wood chips, soil was also properly supplied with water and nutrients. The bioaugumantation seems to enhance biodegradation process. After 5 months, 93% of non-polar compounds were eliminated from soil containing immobilized biomass. Comparatively, in non-treated soil (control system) the contaminant elimination was at the level of 47%. Bacterial number in treated and non-treated soil was similar for about 3 months; however enzymatic activity (dehydrogenascs and hydrolascs) in control soil was much lower. Finally, after 5 months of treatment the content of bacteria active in contaminant decomposition in inoculated soil was 100-fold higher than in control system. Presumably, the main reason of low remediation results in non-treated soil seems to be low enzymatic activity of the biomass.
Go to article

Authors and Affiliations

Ewa Zborowska
Jeremi Naumczyk
Ewelina Bugryn
Renata Wojciechowska
Download PDF Download RIS Download Bibtex

Abstract

Surfactants can interfere with the biological wastewater treatment processes. They contribute to the changes in activated sludge floes structure. In order to quantify the influence of surfactants on sludge floes morphology the series of experiments in the flow continuous system were conducted. Sodium dodccyl sulphate, which belongs to the most ubiquitous anionic surfactant in everyday use, was selected to be the object of investigations. The results of its biodegradation in continuous flow system at influent concentration of 250 mg -dm' are presented. It turned out that SDS diminished the mean projected area of floes from 50 OOO to 15 OOO μm' with the increase of dilution rate from 0.029 to 0.192 h·1• At the same time the obtained data confirmed that there was a correlation between the morphological parameters of floes and other biomass indicators. The linear relation between mean projected area of floes and volatile suspended solids was found.
Go to article

Authors and Affiliations

Ewa Liwarska--Bizukojc
Marcin Bizukojc
Download PDF Download RIS Download Bibtex

Abstract

Studies on packaging made of polylactide (PLA) subjected to long-term influence of soil environment conditions have been presented in this paper. The scientific objective of this study was to determine changes in selected properties of the PLA packaging after long-term incubation in soil. These changes were investigated by scanning electron microscopy, differential scanning calorimetry, thermogravimetric analysis, and gel permeation chromatography. The structure, thermal properties, and disintegration degree of the packaging after their three-year incubation in soil have been discussed. It was found that the PLA packaging did not disintegrate significantly in the soil environment, and slight changes in their structure and lack of significant changes in thermal properties indicate that the efficiency of their degradation in soil conditions after three years is very low. This was mainly due to inadequate temperatures in the soil. It was also found (based on the results of scanning electron microscopy and gel permeation chromatography) that initiation of the biodegradation process took place and that this process is much faster than in the case of conventional non-biodegradable polymers. The results are confirmation that materials obtained of various biodegradable polymers (not only PLA) should be biodegradable only under strictly defined conditions, allocated to a specific type of polymer, i.e. those in which they are easily and quickly biodegradable
Go to article

Bibliography

  1. Adhikari, D., Mukai, M., Kubota, K., Kai, T., Kaneko, N., Araki, K.S. & Kubo, M. (2016). Degradation of Bioplastics in Soil and Their Degradation Effects on Environmental Microorganisms, Journal of Agricultural Chemistry and Environment, 5, pp. 23-34. DOI:10.4236/jacen.2016.51003
  2. Ahmed, J. & Varshney, S.K. (2011). Polylactides – Chemistry, Properties and Green Packaging Technology: A Review, International Journal of Food Properties, 14, pp. 37-58. DOI:10.1080/10942910903125284
  3. Bhagwat, G., Gray, K., Wilson, S.P., Muniyasamy, S., Vincent, S.G.T., Bush, R. & Palanisami, T. (2020). Benchmarking Bioplastics: A Natural Step Towards a Sustainable Future, Journal of Polymers and the Environment, 28, pp. 3055-3075. DOI:10.1007/s10924-020-01830-8
  4. Deroiné, M., Le Duigou, A., Corre, Y.M., Le, Gac, P.Y., Davies, P., César, G. & Bruzaud, S. (2014). Accelerated ageing of polylactide in aqueous environments: Comparative study between distilled water and seawater, Polymer Degradation and Stability, 108, pp. 319-329. DOI:10.1016/j.polymdegradstab.2014.01.020
  5. Dintcheva, N.T., Al-Malaika, S., Morici, E. & Arrigo, R. (2017). Thermo-oxidative stabilization of poly(lactic acid)-based nanocomposites through the incorporation of clay with in-built antioxidant activity, Journal of Applied Polymer Science, 134, pp. 44974-44986. DOI:10.1002/app.44974
  6. Donghee, K., Yoshito, A., Yoshihito, S. & Haruo, N. (2011). Biomass-based composites from poly(lactic acid) and wood flour by vapor-phase assisted surface polymerization, ACS Applied Materials & Interfaces, 3, pp. 385-391. DOI:10.1021/am1009953
  7. Fischer, E.W., Sterzel, H.J. & Wegner, G. (1973). Investigation of the structure of solution grown crystals of lactide copolymers by means of chemical reactions, Colloid and Polymer Science, 251, pp. 980-990. DOI:10.1007/BF01498927
  8. Itavaara, M., Karjomaa, S. & Selin, J.F. (2002). Biodegradation of polylactide in aerobic and anaerobic thermophilic conditions, Chemosphere, 46, pp. 879-885. DOI:10.1016/s0045-6535(01)00163-1
  9. Janczak, K., Dąbrowska, G.B., Raszkowska-Kaczor., A., Kaczor, D., Hrynkiewicz, K. & Richert, A. (2020). Biodegradation of the plastics PLA and PET in cultivated soil with the participation of microorganisms and plants, International Biodeterioration & Biodegradation, 155, 105087. DOI:10.1016/j.ibiod.2020.105087
  10. John, R.P., Nampoothiri, K.M. & Pandey, A. (2007). Fermentative production of lactic acid from biomass: an overview on process developments and future perspectives, Applied Microbiology and Biotechnology, 74, pp. 524-534. DOI:10.1007/s00253-006-0779-6
  11. Kale, G., Auras, R. & Singh, S.P. (2007). Comparison of the degradability of poly (lactide ) packages in composting and ambient exposure conditions, Packaging Technology & Science, 20, pp. 49-70. DOI:10.1002/pts.742
  12. Kamiya, M., Asakawa, S. & Kimura, M. (2007). Molecular Analysis of Fungal Communities of Biodegradable Plastics in Two Japanese Soils, Soil Science and Plant Nutrition, 53, pp. 568-574. DOI:10.1111/j.1747-0765.2007.00169.x
  13. Kim, M.N., Kim, W.G., Weon, H.Y. & Lee, S.H. (2008). Poly(L-Lactide)-Degrading Activity of a Newly Isolated Bacterium, Journal of Applied Polymer Science, 109, pp. 234-239. DOI:10.1002/app.26658
  14. Kim, D.Y. & Rhee, Y.H. (2003). Biodegradation of Microbial and Synthetic Polyesters by Fungi, Applied Microbiology and Biotechonology, 61, pp. 300-308. DOI:10.1007/s00253-002-1205-3
  15. Lee, S.H. & Kim, M.N. (2010). Isolation of Bacteria Degrading Poly(butylenes succinate-co-butylene adipate) and Their lip A Gene, International Biodeterioration and Biodegradation, 64, pp. 184-190. DOI:10.1016/j.ibiod.2010.01.002
  16. Mehlika, K., Ashley, H. & Geoffrey, D.R. (2014). Isolation and characterisation of fungal communities associated with degradation and growth on the surface of poly(lactic) acid (PLA) in soil and compost, International Biodeterioration & Biodegradation, 95, pp. 301-310. DOI:10.1016/j.ibiod.2014.09.006
  17. Nakamura, K., Tomita, T., Abe, N. & Kamio, Y. (2001). Purification and Characterization of an Extracellular Poly(L-Lactic Acid) Depolymerase from a Soil Isolate, Amycolatopsis sp. Strain K104-1, Applied Environmental Microbiology, 67, pp. 345-353. DOI:10.1128/aem.67.1.345-353.2001
  18. PlasticsEurope (2022). Plastics – the Facts 2022, (https://plasticseurope.org/knowledge-hub/plastics-the-facts-2022/ (11.01.2023))
  19. Poluszyńska, J., Ciesielczuk, T., Biernacki, M. & Paciorkowski, M. (2021). The effect of temperature on the biodegradation of different types of packaging materials under test conditions, Archives of Environmental Protection, 47, pp. 74-83. DOI:10.24425/aep.2021.139503
  20. Saadi, Z., Rasmont, A., Cesar, G., Bewa, H. & Benguigui, L. (2012). Fungal degradation of poly(l-lactide) in soil and in compost, Journal of Polymers and the Environment, 20, pp. 273-282. DOI:10.1007/s10924-011-0399-9
  21. Sarasua, J.R., Prud’Homme, R.E., Wisniewski, M., Le Borgne, A. & Spassky, N. (1998). Crystallization and Melting Behavior of Polylactides. Macromolecules, 31, pp. 3895-3905. DOI:10.1021/ma971545p
  22. Satti, S.M., Shah, A.A., Marsh, T.L. & Auras, R. (2018). Biodegradation of Poly(lactic acid) in Soil Microcosms at Ambient Temperature: Evaluation of Natural Attenuation, Bio-augmentation and Bio-stimulation, Journal of Polymers and the Environment, 26, pp. 3848-3857. DOI:10.1007/s10924-018-1264-x
  23. Shah, A.A., Hasan, F., Hameed, A. & Ahmed, S. (2008). Biological Degradation of Plastics: A Comprehensive Review, Biotechnology Advances, 26, pp. 246-265. DOI:10.1016/j.biotechadv.2007.12.005
  24. Siparsky, G.L., Voorhees, K.J., Dorgan, J.R. & Schilling, K. (1997). Water transport in polylactic acid (PLA), PLA/polycaprolactone copolymers, and PLA/polyethylene glycol blends, Journal of Environmental Polymer Degradation, 5, pp. 125-136. DOI:10.1007/BF02763656
  25. Södergard, A., Selin, J.F. & Näsman, J.H. (1996). Hydrolytic degradation of peroxide modified poly(L-lactide), Polymer Degradation and Stability, 51, pp. 351-359. DOI:10.1016/0141-3910(95)00271-5
  26. Sterzyński, T. (2000). Processing and property improvement in isotactic polypropylene by heterogeneous nucleation, Polimery, 45, pp. 786-791.
  27. Teeraphatpornchai, T., Nakajima-Kambe, T., Shigeno-Akutsu, Y., Nakayama, M., Nomura, N., Nakahara, T. & Uchiyama, H. (2003). Isolation and Characterization of a Bacterium That Degrades Various Polyester-Based Biodegradable Plastics, Biotechnology Letters, 25, pp. 23-28. DOI:10.1023/A:1021713711160
  28. Tsuji, H., Tezuka, Y., Saha, S.K., Suzuki, M. & Itsuno, S. (2005). Spherulite growth of l-lactide copolymers: Effects of tacticity and comonomers, Polymer, 46, pp. 4917-4927. DOI:10.1016/j.polymer.2005.03.069
  29. Weir, N.A., Buchanan, F.J., Orr, J.F., Farrar, D.F. & Dickson, G.R. (2004). Degradation of poly-L-lactide. Part 2: increased temperature accelerated degradation, Proceedings of the Institution of Mechanical Engineers, Part H: Journal of Engineering in Medicine, 218, pp. 321-330. DOI:10.1243/0954411041932809
  30. Żenkiewicz, M., Malinowski, R., Rytlewski, P., Richert, A., Sikorska, W. & Krasowska, K. (2012). Some composting and biodegradation effects of physically or chemically crosslinked poly(lactic acid), Polymer Testing, 31, pp. 83-92. DOI:10.1016/j.polymertesting.2011.09.012
Go to article

Authors and Affiliations

Rafał Malinowski
1
ORCID: ORCID
Marta Musioł
2
ORCID: ORCID
Krzysztof Moraczewski
3
Volodymyr Krasinskyi
1
ORCID: ORCID
Lauren Szymańska
1
ORCID: ORCID
Krzysztof Bajer
1
ORCID: ORCID

  1. Łukasiewicz Research Network - Institute for Engineering of Polymer Materials and Dyes, Toruń, Poland
  2. Centre of Polymer and Carbon Materials, Polish Academy of Sciences, Zabrze, Poland
  3. Faculty of Materials Engineering, Kazimierz Wielki University, Bydgoszcz, Poland
Download PDF Download RIS Download Bibtex

Abstract

Polycyclic aromatic hydrocarbons (PAHs) are significant pollutants found in petroleum products. There is ample literature on the biodegradation of PAHs containing less than five rings, but little has been done on those with more than five rings. Coronene (CRN), a seven-ring-containing PAH, has only been shown to be degraded by one bacterial strain. In this study, a bacterial strain 10SCRN4D was isolated through enrichment in the presence of CRN and 10% NaCl (w/v). Analysis of the 16S rRNA gene identified the strain as Halomonas caseinilytica. The strain was able to degrade CRN in media containing 16.5–165 μM CRN with a doubling time of 9–16 hours and grew in a wide range of salinity (0.5–10%, w/v) and temperature (30–50°C) with optimum conditions of pH 7, salinity 0.5%–10% (w/v), and temperature 37°C. Over 20 days, almost 35% of 16.5 μM CRN was degraded, reaching 76% degradation after 80 days as measured by gas chromatography. The strain was also able to degrade smaller molecular weight PAHs such as benzo[a]pyrene, pyrene, and phenanthrene. This is the first report of Halomonas caseinilytica degrading CRN as the sole carbon source in high salinity, and thus highlights the potential of this strain in bioremediation.
Go to article

Bibliography


  1. Abbasian, F., Lockington, R., Mallavarapu, M. & Naidu, R. (2015). A Comprehensive Review of Aliphatic Hydrocarbon Biodegradation by Bacteria. Appl Biochem Biotechnol 176, pp. 670–699. DOI:10.1007/s12010-015-1603-5.
  2. Al-Awadhi, H., Sulaiman, R. H. D., Mahmoud, H. M. & Radwan, S. S. (2007). Alkaliphilic and halophilic hydrocarbon-utilizing bacteria from Kuwaiti coasts of the Arabian Gulf. Appl Microbiol Biotechnol 77, pp. 183–186. DOI:10.1007/s00253-007-1127-1.
  3. Alva, V. A. & Peyton, B. M. (2003). Phenol and Catechol Biodegradation by the Haloalkaliphile Halomonas campisalis: Influence of pH and Salinity. Environ Sci Technol 37, pp. 4397–4402. DOI:10.1021/es0341844.
  4. Anonymous (2023). Team, R: A Language and Environment for Statistical Computing, 2023 (R Foundation for Statistical Computing: Vienna). 10 Feb 2023. Available at: http://www.r-project.org/index.html.
  5. Arulazhagan, P. & Vasudevan, N. (2011). Biodegradation of polycyclic aromatic hydrocarbons by a halotolerant bacterial strain Ochrobactrum sp. VA1. Mar Pollut Bull 62, pp. 388–394. DOI:10.1016/j.marpolbul.2010.09.020.
  6. Baali, A. & Yahyaoui, A. (2019). “Polycyclic Aromatic Hydrocarbons (PAHs) and Their Influence to Some Aquatic Species,” in Biochemical Toxicology, eds. M. Ince, O. K. Ince, and G. Ondrasek (Rijeka: IntechOpen), Ch. 12. DOI:10.5772/intechopen.86213.
  7. Bamforth, S. M. & Singleton, I. (2005). Review bioremediation of polycyclic aromatic hydrocarbons: Current knowledge and future directions. J.Chem.Techn. Biotechn 80, pp. 723–736.
  8. Budiyanto, F., Thukair, A., Al-Momani, M., Musa, M. M. & Nzila, A. (2018). Characterization of Halophilic Bacteria Capable of Efficiently Biodegrading the High-Molecular-Weight Polycyclic Aromatic Hydrocarbon Pyrene. Environ Eng Sci 35. DOI:10.1089/ees.2017.0244.
  9. Cheffi, M., Hentati, D., Chebbi, A., Mhiri, N., Sayadi, S., Marqués, A. & Chamkha, M. (2020). Isolation and characterization of a newly naphthalene-degrading Halomonas pacifica, strain Cnaph3: biodegradation and biosurfactant production studies. 3 Biotech 10. DOI:10.1007/s13205-020-2085-x.
  10. Chen, C., Anwar, N., Wu, C., Fu, G., Wang, R., Zhang, C., Wu, Y., Sun, C & Wu, M. (2018). Halomonas endophytica sp. nov., isolated from liquid in the stems of Populus euphratica. Int J Syst Evol Microbiol 68, pp. 1633–1638. DOI:10.1099/ijsem.0.002585.
  11. Dhar, K., Subashchandrabose, S. R., Venkateswarlu, K., Krishnan, K. & Megharaj, M. (2020). Anaerobic Microbial Degradation of Polycyclic Aromatic Hydrocarbons: A Comprehensive Review. Rev Environ Contam Toxicol 251, pp. 25–108. DOI:10.1007/398_2019_29.
  12. Dore, S. Y., Clancy, Q. E., Rylee, S. M. & Kulpa Jr., C. F. (2003). Naphthalene-utilizing and mercury-resistant bacteria isolated from an acidic environment. Appl Microbiol Biotechnol 63, pp. 194–199. DOI:10.1007/s00253-003-1378-4.
  13. Ghosal, D., Ghosh, S., Dutta, T. K. & Ahn, Y. (2016). Current State of Knowledge in Microbial Degradation of Polycyclic Aromatic Hydrocarbons (PAHs): A Review. Front Microbiol 7, 1369. DOI:10.3389/fmicb.2016.01369.
  14. Govarthanan, M., Khalifa, A. Y. Z., Kamala-Kannan, S., Srinivasan, P., Selvankumar, T., Selvam, K. & Kim, W. (2020). Significance of allochthonous brackish water Halomonas sp. on biodegradation of low and high molecular weight polycyclic aromatic hydrocarbons. Chemosphere 243, 125389. DOI:10.1016/j.chemosphere.2019.125389.
  15. Habe, H., Kanemitsu, M., Nomura, M., Takemura, T., Iwata, K., Nojiri, H., Yamane, H. & Omori, T. (2004). Isolation and characterization of an alkaliphilic bacterium utilizing pyrene as a carbon source. J Biosci Bioeng 98, pp. 306–308. DOI:10.1016/S1389-1723(04)00287-7.
  16. Hajizadeh, N., Sefidi Heris, Y., Zununi Vahed, S., Vallipour, J., Hejazi, M., Golabi, S., Asadpour-Zeynali, K. & Hejazi, M.S. (2015). Biodegradation of Para-Amino Acetanilide by Halomonas sp. TBZ3. Jundishapur J Microbiol 8. DOI:10.5812/jjm.18622.
  17. Harrison, J., Hallsworth, J. & Cockell, C. (2015). Reduction of the Temperature Sensitivity of Halomonas hydrothermalis by Iron Starvation Combined with Microaerobic Conditions. Appl Environ Microbiol 81, pp. 2156–2162. DOI:10.1128/AEM.03639-14.
  18. Juhasz, A. L., Britz, M. L. & Stanley, G. A. (1996). Degradation of high molecular weight polycyclic aromatic hydrocarbons by Pseudomonas cepacia. Biotechnol Lett 18, pp. 577–582. DOI:10.1007/BF00140206.
  19. Juhasz, A. L., Britz, M. L. & Stanley, G. A. (1997). Degradation of benzo[a]pyrene, dibenz[a,h]anthracene and coronene by Burkholderia cepacia. Water Science and Technology 36, pp. 45–51. DOI:10.1016/S0273-1223(97)00641-0.
  20. Juhasz, A. L., Stanley, G. A. & Britz, M. L. (2000). Microbial degradation and detoxification of high molecular weight polycyclic aromatic hydrocarbons by Stenotrophomonas maltophilia strain VUN 10,003. Lett Appl Microbiol 30, pp. 396–401. DOI:10.1046/j.1472-765x.2000.00733.x.
  21. Kaye, J. Z., Márquez, M. C., Ventosa, A. & Baross, J. A. (2004). Halomonas neptunia sp. nov., Halomonas sulfidaeris sp. nov., Halomonas axialensis sp. nov. and Halomonas hydrothermalis sp. nov.: halophilic bacteria isolated from deep-sea hydrothermal-vent environments. Int J Syst Evol Microbiol 54, pp. 499–511. DOI:10.1099/ijs.0.02799-0.
  22. Lawal, A. T. (2017). Polycyclic aromatic hydrocarbons. A review. Cogent Environ Sci 3, 1339841. DOI:10.1080/23311843.2017.1339841.
  23. Leahy, J. G. & Colwell, R. R. (1990). Microbial degradation of hydrocarbons in the environment. Microbiol Rev 54, pp. 305–315. Available at: http://www.ncbi.nlm.nih.gov/pmc/articles/PMC372779/.
  24. Lee, B.-K. & v Vu, T. (2010). “Sources, Distribution and Toxicity of Polyaromatic Hydrocarbons (PAHs) in Particulate Matter,” in Air Pollution DOI:10.5772/10045.
  25. Lima, A. L. C., Farrington, J. W. & Reddy, C. M. (2005). Combustion-Derived Polycyclic Aromatic Hydrocarbons in the Environment—A Review. Environ Forensics 6, pp. 109–131. DOI:10.1080/15275920590952739.
  26. Margesin, R. & Schinner, F. (2001). Biodegradation and bioremediation of hydrocarbons in extreme environments. Appl Microbiol Biotechnol 56, pp. 650–663. DOI:10.1007/s002530100701.
  27. Ming, H., Ji, W., Li, M., Zhao, Z., Cheng, L., Niu, M., Ling-Yu, Z., Wang, Y. & Guo-Xing, N. (2020). Halomonas lactosivorans sp. nov., isolated from salt-lake sediment. Int J Syst Evol Microbiol 70, pp. 3504–3512. DOI:10.1099/ijsem.0.004209.
  28. Nzila, A. (2018). Biodegradation of high-molecular-weight polycyclic aromatic hydrocarbons under anaerobic conditions: Overview of studies, proposed pathways and future perspectives. Environ Pollut 239, pp. 788–802. DOI:10.1016/j.envpol.2018.04.074.
  29. Nzila, A. & Musa, M. M. (2020). Current Status of and Future Perspectives in Bacterial Degradation of Benzo[a]pyrene. Int J Environ Res Public Health 18. DOI:10.3390/ijerph18010262.
  30. Nzila, A., Musa, M. M., Sankara, S., Al-Momani, M., Xiang, L. & Li, Q. X. (2021). Degradation of benzo[a]pyrene by halophilic bacterial strain Staphylococcus haemoliticus strain 10SBZ1A. PLoS One 16, e0247723. DOI:10.1371/journal.pone.0247723.
  31. Nzila, A., Ramirez, C. O. C. O., Musa, M. M. M., Sankara, S., Basheer, C. & Li, Q. X. Q. X. (2018). Pyrene biodegradation and proteomic analysis in Achromobacter xylosoxidans, PY4 strain. Int Biodeterior Biodegradation 130, pp. 40–47. DOI:10.1016/j.ibiod.2018.03.014.
  32. Nzila, A., Sankara, S., Al-Momani, M., Musa Musa, M. & Musa, M. M. (2017). Isolation and characterisation of bacteria degrading polycyclic aromatic hydrocarbons: phenanthrene and anthracene. Arch Environ Prot 44, pp. 43–54. DOI:10.1515/aep-2016-0028.
  33. Patel, A. B., Shaikh, S., Jain, K. R., Desai, C. & Madamwar, D. (2020). Polycyclic Aromatic Hydrocarbons: Sources, Toxicity, and Remediation Approaches. Front Microbiol 11. Available at: https://www.frontiersin.org/articles/10.3389/fmicb.2020.562813.
  34. Pohl, A. & Kostecki, M. (2020). Spatial distribution, ecological risk and sources of polycyclic aromatic hydrocarbons (PAHs) in water and bottom sediments of the anthropogeniclymnic ecosystems under conditions of diversified anthropopressure. Archives of Environmental Protection 46, pp. 104–120. DOI:10.24425/aep.2020.135769.
  35. Qin, W., Fan, F., Zhu, Y., Huang, X., Ding, A., Liu, X. & Dou, J. (2018). Anaerobic biodegradation of benzo(a)pyrene by a novel Cellulosimicrobium cellulans CWS2 isolated from polycyclic aromatic hydrocarbon-contaminated soil. Braz J Microbiol 49, pp. 258–268. DOI:10.1016/j.bjm.2017.04.014.
  36. Stapleton, R. D., Savage, D. C., Sayler, G. S. & Stacey, G. (1998). Biodegradation of aromatic hydrocarbons in an extremely acidic environment. Appl Environ Microbiol 64, pp. 4180–4184. DOI:10.1128/AEM.64.11.4180-4184.1998.
  37. Swaathy, S., Kavitha, V., Pravin, A. S., Mandal, A. B. & Gnanamani, A. (2014). Microbial surfactant mediated degradation of anthracene in aqueous phase by marine Bacillus licheniformis MTCC 5514. Biotechnology Reports 4, pp. 161–170. DOI:10.1016/j.btre.2014.10.004.
  38. Wenting, R., Montazersaheb, S., Khan, S. A., Kim, H. M., Tarhriz, V., Hejazi, M. A. & Che, O.O. (2021). Halomonas azerica sp. nov., Isolated from Urmia Lake in Iran. Curr Microbiol 78, pp. 3299–3306. DOI:10.1007/s00284-021-02482-0.
  39. Włodarczyk-Makuła, M. (2012). Half-Life of Carcinogenic Polycyclic Aromatic Hydrocarbons in Stored Sewage Sludge. Archives of Environmental Protection 38. DOI:10.2478/v10265-012-0016-6.
  40. Wu, Y., He, T., Zhong, M., Zhang, Y., Li, E., Huang, T. & Hu, Z. (2009). Isolation of marine benzo[a]pyrene-degrading Ochrobactrum sp. BAP5 and proteins characterization. Journal of Environmental Sciences 21, pp. 1446–1451. DOI:10.1016/S1001-0742(08)62438-9.
  41. Wu, Y.-H., Xu, X.-W., Huo, Y.-Y., Zhou, P., Zhu, X.-F., Zhang, H.-B. & Wu, M. (2008). Halomonas caseinilytica sp. nov., a halophilic bacterium isolated from a saline lake on the Qinghai-Tibet Plateau, China. Int J Syst Evol Microbiol 58, pp. 1259–1262. DOI:10.1099/ijs.0.65381-0.
  42. Xiao-Ran, J., Jin, Y., Xiangbin, C. & Guo-Qiang, C. (2018). “Chapter Eleven - Halomonas and Pathway Engineering for Bioplastics Production,” in Methods in Enzymology, ed. N. Scrutton (Academic Press), pp. 309–328. DOI:10.1016/bs.mie.2018.04.008.
  43. Xu, L., Ying, J.-J., Fang, Y.-C., Zhang, R., Hua, J., Wu, M., Han, B-N. & Sun, C. (2021). Halomonas populi sp. nov. isolated from Populus euphratica. Arch Microbiol 204, 86. DOI:10.1007/s00203-021-02704-w.
  44. Ye, J.-W. & Chen, G.-Q. (2021). Halomonas as a chassis. Essays Biochem, 65(2), pp. 393-403. DOI:10.1042/EBC20200159.
  45. Yessica, G.-P., Alejandro, A., Ronald, F.-C., José, A. J., Esperanza, M.-R., Samuel, C.-S. J., Mendoza-Lopes, M.R & Ormeño-Orrillo, E. (2013). Tolerance, growth and degradation of phenanthrene and benzo[a]pyrene by Rhizobium tropici CIAT 899 in liquid culture medium. Applied Soil Ecology 63, pp. 105–111. DOI: 10.1016/j.apsoil.2012.09.010.
  46. Yin, J., Chen, J.-C., Wu, Q. & Chen, G.-Q. (2015). Halophiles, coming stars for industrial biotechnology. Biotechnol Adv 33, pp. 1433–1442. DOI:10.1016/j.biotechadv.2014.10.008.
Go to article

Authors and Affiliations

Ajibola H. Okeyode
1
Assad Al-Thukair
1
Basheer Chanbasha
2 3
Mazen K. Nazal
4
Emmanuel Afuecheta
5 6
Musa M. Musa
2 7
ORCID: ORCID
Shahad Algarni
1
Alexis Nzila
1 3

  1. Department of Bioengineering, King Fahd University of Petroleum and Minerals Dhahran, Saudi Arabia,
  2. Department of Chemistry, King Fahd University of Petroleum and Minerals, Dhahran, Saudi Arabia
  3. Interdisciplinary Research Center for Membranes and Water Security, King Fahd University ofPetroleum and Minerals, Dhahran, Saudi Arabia
  4. Applied Research Center for Environment and Marine Studies, Research Institute, King Fahd Universityof Petroleum and Minerals, Dhahran, Saudi Arabia
  5. Departments of Mathematics, King Fahd University of Petroleum and Minerals, Dhahran 31261, SaudiArabia
  6. Interdisciplinary Research Center for Finance and Digital Economy, KFUPM, Dhahran, Saudi Arabia
  7. Interdisciplinary Research Center for Refining and Advanced Chemicals, King Fahd University ofPetroleum and Minerals, Dhahran 31261, Saudi Arabia
Download PDF Download RIS Download Bibtex

Abstract

Many paper-related products are in daily use all over the world. Although paper is one of the most recycled materials in the European Union, no end-of-waste criteria have been defi ned. Typical paper and cardboard should be recycled, but paper materials with impurities, such as cooking oil, sand, or plastic, are much more problematic. In particular, paper contaminated with cooking oil or butter (e.g., pizza boxes) is diffi cult waste. Also baking parchment paper cannot be stored as waste paper after use. Composting could be a solution, but in many municipal solid waste collection systems, this waste types are collected with the mixed waste stream, what fi nally leads this material to landfi lling or incinerating processes. Parchment paper and pizza box cardboard contain a lot of cellulose and in landfi lls are a source of CO2 and CH4. Incineration of these materials also leads to CO2 emission. The aim of this study was to investigate the degradation of cooking-oil-contaminated paper in media with a low inorganic nitrogen content. Cardboard usually used for packaging purposes was used as pre-test material. Two types of paper usually used in the kitchen were used: pizza box cardboard and parchment paper highly contaminated with cooking oil. Two types of low inorganic nitrogen media were tested: mature municipal waste compost (MSWC) and leaf mold (LM). The decrease of mass of both paper sample types was correlated with process time. Both tested sample types: dry cellulose materials and paper with cooking oil added, were partly or completely decomposed after 6 weeks of bioprocessing in aerobic conditions without an additional dose of inorganic nitrogen. According to waste separation rules, wet paper or paper contaminated with cooking oil have to be stored with other wastes which are „not possible for further use”. This work show possibility to change these rules.
Go to article

Bibliography

  1. Agarwal, G., Liu, G. & Lattimer, G. (2014) Pyrolysis and Oxidation of Cardboard. Fire safety science-proceedings of the eleventh international symposium. pp. 124–137. DOI:10.3801/IAFSS. FSS.11-124
  2. Ahmed, S., Hall, A.M. & Ahmed, S.F. (2018) Biodegradation of Different Types of Paper in a Compost Environment. Proceedings of the 5th International Conference on Natural Sciences and Technology (ICNST’18) March 30–31, Asian University for Women, Chittagong, Bangladesh.
  3. Al-Mutairi, N. (2009) Co-composting of manure with fat, oil, and grease: Microbial fingerprinting and phytotoxicity evaluation. Can. J. Civ. Eng. 36(2) pp. 209–218. DOI:10.1139/L08-117
  4. Aluyor, E.O., Obahiagbon, K.O. & Ori-jesu, M. (2009) Biodegradation of vegetable oils: A review. Scientific Research and Essay, 4(6), pp. 543–54.
  5. Andlar, M., Rezic, T., Mardetko, M., Kracher, D., Ludwig, R. & Santek B. (2018) Lignocellulose degradation: An overview of fungi and fungal enzymes involved in lignocellulose degradation. Engineering in Life Sciences, 18 pp. 768–778. DOI:10.1002/ elsc.201800039
  6. Balada, I., Altmann, V. & Šařec, P. (2016) Material waste paper recycling for the production of substrates and briquettes. Agronomy Research 14(3), pp. 661–671.
  7. Bekiroğlu, S., Elmas, G.M. & Yagshiyev, Y. (2017) Contribution to Sustainability and the National Economy Through Recycling Waste Paper from Istanbul’s Hotels in Turkey. BioResources, 12(4), pp. 6924–6955. DOI:10.15376/biores.12.4.6924-6955
  8. Bogaard, J. & Whitmore, P.M. (2002) Explorations of the role of humidity fluctuations in the deterioration of paper. Studies in Conservation, 47(3), pp. 11–15. DOI:10.1179/sic.2002.47.s3.003
  9. Borrego, S., Gómez de Saravia, S., Valdés, O., Vivar, I., Battistoni, P. & Guiamet, P. (2016) Biocidal activity of two essential oils on fungi that cause degradation of paper documents. International Journal of Conservation Science, 7(2), pp. 369–380.
  10. Cichosz, G. & Czeczot, H. (2011) Oxidative stability of edible fats – consequences to human health. Bromat. Chem. Toksykol. XLIV, 1, pp. 50–60
  11. Ciesielczuk, T., Poluszyńska, J., Rosik-Dulewska, Cz., Sporek, M. & Lenkiewicz, M. (2016). Uses of weeds as an economical alternative to processed wood biomass and fossil fuels. Ecological engineering, 95, pp. 485–491. DOI:10.1016/j.ecoleng.2016.06.100
  12. Cuvelier, M.E., Soto, P., Courtois, F., Broyart, B. & Bonazzi, C. (2017) Oxygen solubility measured in aqueous or oily media by a method using a non-invasive sensor. Food Control, 73, part 3, pp. 1466–1473. DOI:10.1016/j.foodcont.2016.11.008
  13. Franica, M., Grzeja, K. & Paszula, S. (2018) Evaluation of quality parameters of selected composts. Archives of Waste Management and Environmental Protection, 20(1), pp. 21–32.
  14. Ghehsareh, M.G., Khosh-Khui, M. & Nazari, F. (2011) Comparison of Municipal Solid Waste Compost, Vermicompost and Leaf Mold on Growth and Development of Cineraria (Pericallis × hybrida ‘Star Wars’). Journal of Applied Biological Sciences, 5 (3), 55–58.
  15. Gumienna, M., & Czarnecki, Z. (2010). The surface-active compounds of microbiological origin. Nauka Przyr. Technol., 4, 4, #51. (in Polish)
  16. Kaakinen, J., Vahaoja, P., Kuokkanen, T. & Roppola, K. (2007) Studies on the Effects of Certain Soil Properties on the Biodegradation of Oils Determined by the Manometric Respirometric Method. J. Automated Methods and Management in Chemistry, 034601. DOI:10.1155/2007/34601
  17. Karahan, S. (2020) Investigation of Recycling Possibilities of Stacked Waste Office Paper for at Least Five Years. GUSTIJ, 10(2) pp. 366 – 373. DOI:10.17714/gumusfenbil.606061
  18. Li, Z., Wrenn, B.A. & Venosa, A.D. (2005) Anaerobic biodegradation of vegetable oil and its metabolic intermediates in oil-enriched freshwater sediments. Biodegradation 16, pp. 341–352. DOI:10.1007/s10532-004-2057-6
  19. Micales, J.A., & Skog, K.E. (1997) The Decomposition of Forest Products in Landfills. International Biodeterioration & Biodegradation, 39, 2–3, pp. 145–158.
  20. Nowińska, A., Baranowska, J. & Malinowski, M. (2019) The analysis of biodegradation process of selected paper packaging waste. Infrastructure And Ecology Of Rural Areas 3, pp. 253–261. DOI:10.14597/INFRAECO.2019.3.1.018
  21. Osono, T. (2019) Functional diversity of ligninolytic fungi associated with leaf litter decomposition. Ecological Research, 35, pp.30–43. DOI:10.1111/1440-1703.12063
  22. Ozimek, A. & Kopeć, M. (2012). Assessment of biological activity of biomass at different stages of composting process with use of the oxitop control measurement system. Acta Agrophysica, 19(2), 379–390.
  23. Perez, J., Munoz-Dorado, J., Rubia, T. & d.l. Martınez, J. (2002) Biodegradation and biological treatments of cellulose, hemicellulose and lignin: An overview. International Microbiology, 5 (2), pp. 53–63. DOI:10.1007/s10123-002- 0062-3
  24. Poluszyńska, J., Ciesielczuk, T., Biernacki, M. & Paciorkowski M. (2021) The effect of temperature on the biodegradation of different types of packaging materials under test conditions. Archives of Environmental Protection, 47(4), pp. 74–83. DOI:10.24425/aep.2021.139503
  25. Rajae, A., Ghita, A.B., Souabi, S., Winterton, P., Cegarra, J. & Hafidi M. (2008) Aerobic biodegradation of sludge from the effluent of a vegetable oil processing plant mixed with household waste: Physical–chemical, microbiological, and spectroscopic analysis. Bioresource technology, 99(18), pp. 8571–8577. DOI:10.1016/j. biortech.2008.04.007
  26. Saletes, S., Siregar, F.A., Caliman, J.P. & Liwang, T. (2004) Ligno- Cellulose Composting: Case Study on Monitoring Oil Palm Residuals. Compost Science & Utilization, 12(4), pp. 372–382. DOI:10.1080/1065657X.2004.10702207
  27. Salihu, I., Mohd, Y.S., Nur, A.Y. & Siti, A.A. (2018) Microbial degradation of vegetable oils: a review, 3, pp. 45–55.
  28. Smirnova. I.E. & Saubenova, M.G. (2001) Use of Cellulose- -Degrading Nitrogen-Fixing Bacteria in the Enrichment of Roughage with Protein. Applied Biochemistry and Microbiology, 37(1), pp. 76–79.
  29. Wan Razali, W.A., Baharuddin, A.S., Talib, A.T., Sulaiman, A., Naim, M.N., Hassan, M.A. & Shirai, Y. (2012) Degradation of oil palm empty fruit bunches (OPEFB) fibre during composting process using in-vessel composter. Bioresources, 7(4), pp. 4786–4805.
  30. Wołczyński, M. & Janosz-Rajczyk, M. (2014) Influence of Initial Alkalinity of Lignocellulosic Waste on Their Enzymatic Degradation. Archives of Environmental Protection, 40(2), pp. 103–113. DOI:10.2478/aep-2014-0019
Go to article

Authors and Affiliations

Tomasz Ciesielczuk
1
ORCID: ORCID
Czesława Rosik-Dulewska
2
ORCID: ORCID

  1. Opole University, Poland
  2. Institute of Environmental Engineering, Polish Academy of Sciences, Zabrze, Poland

This page uses 'cookies'. Learn more