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Abstract

In this work, an assessment and comparison of the quality of selected bentonites and bentonite mixtures was made. The samples consisted of available foundry materials used for bonding green sands. Determining the homogeneity degree and specific surface area of the grains allowed us to compare the examined materials and determine their influence on other parameters. On the basis of a thermal analysis of the bentonites or bentonite mixtures, the changes occurring in the sample during its heating were determined. Determining the potential for ion exchange and montmorillonite content enabled us to assess the binding properties of the materials. The preparation of six green sands with different bentonites or bentonite mixtures gave us the opportunity to assess the changes in apparent density, permeability, compressive strength and friability as a function of humidity, and the impact of different materials on the mentioned parameters. Their charts were analyzed, and the molding sand with the addition of bentonite or a bentonite mixture was selected for which these parameters are favorable. On this basis, the best-presented binding material was assessed and selected.

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Authors and Affiliations

S. Paź
D. Drożyński
M. Górny
S. Cukrowicz
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Abstract

Until now, the mould sand in general use in the foundry industry are based on bentonite, which resulted from the fact that a good recognition properties and phenomena associated with this material. Come to know and normalized content of montmorillonite and carbonates and their important role in the construction of bentonite, and mass properties of the participation of compressive strength or scatter. Halloysite is widely used in industry and beyond them. However, little is known about its use in the foundry in Poland and abroad. This article presents preliminary research conducted at the Foundry Department of Silesian University of Technology on this material. Will raise the question of the representation of this two materials, which contains information connected with history and formation of materials, their structure and chemical composition. In the research, the results of compressive strength tests in wet masses of quartz matrix, where as a binder is used halloysite and bentonite in different proportions.

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Authors and Affiliations

M. Cholewa
Ł. Kozakiewicz
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Abstract

Bentonites and clays are included in the group of drilling fluids materials. The raw materials are mainly clay minerals, which are divided into several groups, like montmorillonite, kaolinite, illite, biotite, muscovite, nontronite, anorthoclase, microcline, sanidine or rutile, differing in chemical composition and crystal lattice structure. Clay minerals have a layered structure forming sheet units. The layers merge into sheets that build up to form the structure of the mineral.

The aim of the studies carried out in the ŁUKASIEWICZ Research Network - Foundry Research Institute is to explore the possibility of using minerals coming from Polish deposits.

The article outlines the basic properties of hybrid bentonites, which are a mixture of bentonite clay called beidellite, originating from overburden deposits of the Turoszów Mine, and foundry bentonite from one of the Slovak deposits. As part of the physico-chemical tests of minerals, measurements included in the PN-85/H-11003 standard, i.e. montmorillonite content, water content and swelling index, were carried out. Additionally, the loss on ignition and pH chemical reaction were determined. Based on the thermal analysis of raw materials, carried out in the temperature range from 0 to 1000oC, changes occurring in these materials during heating, i.e. thermal stability in contact with liquid metal, were determined.

Examinations of the sand mixture based on pure clay and bentonite and of the sand mixture based on hybrid bentonites enabled tracing changes in permeability, compressive strength and tensile strength in the transformation zone as well as compactability referred to the clay content in sand mixture. Selected technological and strength parameters of synthetic sands are crucial for the foundry, because they significantly affect the quality of the finished casting.

Based on the analysis of the results, the optimal composition of hybrid bentonite was selected.

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Authors and Affiliations

J. Kamińska
ORCID: ORCID
S. Puzio
ORCID: ORCID
M. Angrecki
ORCID: ORCID
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Abstract

Bentonite is clay rock, which is created by decomposition of vulcanic glass. It is formed from mixture of clay minerals of smectite group,

mainly montmorillonite, beidellite and nontronite. Its typical characteristics is, that when in contact with water, it intensively swells. First

who used this term was W.C. Knight in 1887. The rock had been named after town Fort Benton in American state Montana. For its

interesting technological properties and whiteness has wide technological use. Bentonite is selectively mined and according to its final use

separately modified, which results in high quality product with specific parameters.

In the beginning of 21st century belong bentonite moulding mixtures in foundry to always perspective. Mainly increased ratio of ductile

cast iron castings production cannot be ensured without the need of quality bentonite. Great area of scope remains to further research of

moulding materials, which return also to bentonite producers.

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Authors and Affiliations

I. Vasková
M. Hrubovčáková
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Abstract

Casting quality depends on many factors including the quality of the input materials, technology, material securing and last but not least, the mould into which the casting is casted. By pouring into a single-shot mould, based mainly on 1st generation binders, is is a very important factor. Basically, a bentonite mixture represents either a three- or four-component system, but each component of the system is a heterogeneous substance. This heterogeneity punctuates mainly a non-stationary heat field, presented throughout the whole process of the casting production. The most important component is a binder and in the case of first generation binders mostly bentonites are used - clays that contain minimum of 80% of montmorillonite
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Authors and Affiliations

I. Vasková
D. Fecko
J. Malik
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Abstract

The aim of this study was to evaluate the effect of high doses of calcium bentonite on the blood parameters, anticoccidial activity and intestinal histology of broiler chickens. Three undred and sixty one-day old broilers were distributed into three treatments (T+VE, T-VE, TB )with three replicates. Amprolium was added to the feed of the positive control group, calcium bentonite powder was added to the TB group, and nothing was added to the feed of the T-VE group. Coccidiosis was induced on day 14, the birds were kept until day 49, measurements of the diffe- rent variables started from week 3, blood samples were collected via wing vein, and fecal oocysts were counted from the intestinal contents of each individual bird using the McMaster techni- que. A decrease in feed consumption, body weight gain and conversion ratio was noticed in the calcium bentonite group. Broilers in the calcium bentonite group (TB ) and negative control group (T-VE ) showed clinical signs of coccidiosis (blood in feces) and the number of oocysts in feces increased with time. Histopathological examinations of the affected caeca also demonstrated excessive tissue damage, hemorrhage, the presence of clusters of large schizonts and merozoites in the tissue, and coccidian oocysts in the lumen. Feed conversion was highest in the T+VE group.

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Authors and Affiliations

F.M.F. Hayajneh
A. Abdelqader
M.A. Alnimer
M.A. Abedal-Majed
J. Al-Khazaleh
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Abstract

The aim of this study was to present the results of the examinations of the structure and thermomechanical properties of PA6/NanoBent composite. NanoBent composites composed of minerals from the smectite group (mainly montmorillonite) were used for modification of polyamide 6. PA6 composite with content of 1, 3, 5% of NanoBent was prepared in a Theysohn TSK 75-N twin screw extruder. The samples were prepared using the injection technology by means of a Krauss-Maffei KM65-160 C1 injection molding machine. The samples of composites obtained at different injection temperatures and injection mold temperatures were used for the examinations. Degree of crystallinity was examined using the DSC method whereas the material structure was examined with an optical microscope. DSC studies showed a reduction in the value of the degree of crystallinity with the increasing content of nanofiller in the polymer material. The narrowing of the peak was recorded in the DSC thermograms for nanocomposites with greater percentage of the nanofiller. Dynamical properties of polyamide 6 nanocomposite were also determined in relation to temperature and frequency. The samples were bended at frequencies of 1 Hz and 10 Hz over the temperature range from –100°C to 180°C and the heating rate of 2K/min. A significant increase in storage modulus was observed for PA6 samples with the content of 5% of NanoBent obtained at the injection temperature of 270°C and mold temperature of 70°C. Smaller size of spherulites and arrangement of structural elements in clusters along the line of polymeric material flow in the mold cavity at higher contents of NanoBent were observed during structural examinations of the composites.
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Authors and Affiliations

A. Gnatowski
1
ORCID: ORCID
R. Gołębski
1
ORCID: ORCID
K. Stachowiak
1
ORCID: ORCID

  1. Czestochowa University of Technology, Department of Technology and Automation, 19c Armii Krajowej Ave, 42-201 Czestochowa, Poland
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Abstract

Zinc (II) removal using low-cost sorbents requires a proper process parametric study to determine

its optimal performance characteristics. In this respect, the present study proposes a new modeling and simulation procedure for heavy metal removal system and is carried out to optimize input variables such as initial pH,

adsorbent dosage, and contact time for biosorption of Zinc (II) by using bentonite. The proposed experimental

system is cost-effective and requires less calculation for determining optimal values, i.e., input variables and

their related removal capacity, Rem%. To optimize the adsorption process, cubic spline curve fitting and numerical differentiation techniques are used for required calculations. According to the proposed calculations, the

removal capacity is calculated as 98.66%, while the optimal values are calculated as initial pH – 6.76, adsorbent

dosage – 1.14 g L-1, contact time – 13 minutes. To evaluate the results, full factor experimental design and 3 way

ANOVA test are used for comparison.

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Authors and Affiliations

B. Mesci
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Abstract

A determination of the heating degree of the moulding sand with bentonite on the grounds of simulating investigations with the application of the MAGMA program, constitutes the contents of the paper. To this end the numerical simulation of the temperature distribution in the virtual casting mould was performed. It was assumed that the mould cavity was filled with a moulding sand with bentonite of a moisture content 3,2 % and bentonite content 8 %. A computer simulation can be used for predicting the heating degree of moulding sands with bentonite. Thus, prediction of the active bentonite (montmorillonite) content in individual layers of the overheated moulding sand can be done by means of the simulation. An overheating degree of a moulding sand with bentonite, and thus the bentonite deactivation depends on a temperature of a casting alloy, casting mass, ratio of: masssand : masscasting, moulding sand amount in the mould and contact area: metal – mould (geometry of the casting shape). Generally it can be stated, that the bentonite deactivation degree depends on two main factors: temperature of moulding sand heating and time of its operation.

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Authors and Affiliations

M. Holtzer
R. Dańko
S. Żymankowska-Kumon
J. Lelito
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Abstract

The criteria, with which one should be guided at the assessment of the binding properties of bentonites used for moulding sands, are proposed in the paper. Apart from the standard parameter which is the active bentonite content, the unrestrained growth indicator should be taken into account since it seems to be more adequate in the estimation of the sand compression strength. The investigations performed for three kinds of bentonites, applied in the Polish foundry plants, subjected to a high temperature influences indicate, that the pathway of changes of the unrestrained growth indicator is very similar to the pathway of changes of the sand compression strength. Instead, the character of changes of the montmorillonite content in the sand in dependence of the temperature is quite different. The sand exhibits the significant active bentonite content, and the sand compression strength decreases rapidly. The montmorillonite content in bentonite samples was determined by the modern copper complex method of triethylenetetraamine (Cu(II)-TET). Tests were performed for bentonites and for sands with those bentonites subjected to high temperatures influences in a range: 100-700ºC.
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Authors and Affiliations

S. Żymankowska-Kumon
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Abstract

The paper presents results of measuring thermal conductivity and heat capacity of bentonite foundry sand in temperature range ambient –

900 OC. During the experiments a technical purity Cu plate was cast into the green-sand moulds. Basing on measurements of the mould

temperature field during the solidification of the casting, the temperature relationships of the measured properties were evaluated. It was

confirmed that water vaporization strongly influences thermal conductivity of the moulding sand in the first period of the mould heating by

the poured casting.

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Authors and Affiliations

P.K. Krajewski
W.K. Krajewski
J.S. Suchy
G. Piwowarski
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Abstract

An organobentonite modified with an amphoteric surfactant, tallow dihydroxyethyl betaine (TDHEB), was used as an adsorbent to simultaneously remove Cu(II) and phenol from wastewater. The characteristic of the organobentonite (named TDHEB-bentonite) was analyzed by X-ray diffraction, Fourier-transform infrared spectra and nitrogen adsorption-desorption isotherm. Batch tests were conducted to evaluate the adsorption capacities of TDHEB-bentonite for the two contaminants. Experiment results demonstrated that the adsorption of both contaminants is highly pH-dependent under acidic conditions. TDHEB-bentonite had about 2.0 and 5.0 times higher adsorption capacity toward Cu(II) and phenol, respectively, relative to the corresponding raw Na-bentonite. Adsorption isotherm data showed that the adsorption processes of both contaminants were well described by Freundlich model. Kinetic experiment demonstrated that both contaminants adsorption processes correlated well with pseudo-second-order model. Cu(II) had a negative impact on phenol adsorption, but not vice versa. Cu(II) was removed mainly through chelating with the organic groups (-CH2CH2OH and -COO-) of TDHEB. Otherwise, partition into the organic phase derived from the adsorbed surfactant was the primarily mechanism for phenol removal. Overall, TDHEB-bentonite was a promising adsorbent for removing Cu(II) and phenol simultaneously from wastewater.
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Bibliography

  1. Andronico, M. & Bajda, T. (2019). Modification of Bentonite with Cationic and Nonionic Surfactants: Structural and Textural Features. Materials, 12(22), 3772. DOI:10.3390/ma12223772
  2. Banat, F. A., Al-Bashir, B., Al-Asheh, S. & Hayajneh, O. (2000). Adsorption of phenol by bentonite. Environmental Pollution, 107(3), pp. 391-398. DOI:10.1016/S0269-7491(99)00173-6
  3. Bhattacharyya, K. G. & Gupta, S. S. (2008). Adsorption of a few heavy metals on natural and modified kaolinite and montmorillonite: A review. Advances in Colloid and Interface Science, 140(2), pp. 114-131. DOI:10.1016/j.cis.2007.12.008
  4. Cao, L., Li, Z., Xiang, S., Huang, Z., Ruan, R. & Liu, Y. (2019). Preparation and characteristics of bentonite–zeolite adsorbent and its application in swine wastewater. Bioresource Technology, 284, pp. 448-455. DOI:10.1016/j.biortech.2019.03.043
  5. Chen, H., Zhou, W., Zhu, K., Zhan, H. & Jiang, M. (2004). Sorption of ionizable organic compounds on HDTMA-modified loess soil. Science of The Total Environment, 326(1), pp. 217-223. DOI:10.1016/j.scitotenv.2003.12.011
  6. Chen, Y., Zhang, X., Wang, L., Cheng, X. & Shang, Q. (2020). Rapid removal of phenol/antibiotics in water by Fe-(8-hydroxyquinoline-7-carboxylic)/TiO2 flower composite: Adsorption combined with photocatalysis. Chemical Engineering Journal, 402, 126260. DOI:10.1016/j.cej.2020.126260
  7. Chu, Y., Khan, M. A., Xia, M., Lei, W., Wang, F., Zhu, S. & Yan, X. (2020). Synthesis and micro-mechanistic studies of histidine modified montmorillonite for lead(II) and copper(II) adsorption from wastewater. Chemical Engineering Research and Design, 157, pp. 142-152. DOI:10.1016/j.cherd.2020.02.020
  8. Díaz-Nava, M. C., Olguín, M. T. & Solache-Ríos, M. (2012). Adsorption of phenol onto surfactants modified bentonite. Journal of Inclusion Phenomena and Macrocyclic Chemistry, 74(1), 67-75. DOI:10.1007/s10847-011-0084-6
  9. Fan, H., Zhou, L., Jiang, X., Huang, Q. & Lang, W. (2014). Adsorption of Cu2+ and methylene blue on dodecyl sulfobetaine surfactant-modified montmorillonite. Applied Clay Science, 95, pp. 150-158. DOI:10.1016/j.clay.2014.04.001
  10. Freundlich, H. (1906). Over the adsorption in solution. The Journal of Physical Chemistry A, 57(385471), pp. 1100-1107. DOI:10.1515/zpch-1907-5723
  11. Griffin, R. A. & Shimp, N. F. (1976). Effect of pH on exchange-adsorption or precipitation of lead from landfill leachates by clay minerals. Environmental science & technology, 10(13), pp. 1256-1261. DOI:10.1021/es60123a003
  12. He, Y., Chen, Y., Zhang, K., Ye, W. & Wu, D. (2019). Removal of chromium and strontium from aqueous solutions by adsorption on laterite. Archives of Environmental Protection, 45(3), pp. 11-20. DOI:10.24425/aep.2019.128636
  13. Kong, Y., Wang, L., Ge, Y., Su, H. & Li, Z. (2019). Lignin xanthate resin–bentonite clay composite as a highly effective and low-cost adsorbent for the removal of doxycycline hydrochloride antibiotic and mercury ions in water. Journal of Hazardous Materials, 368, pp. 33-41. DOI:10.1016/j.jhazmat.2019.01.026
  14. Langmuir, I. (1918). The adsorption of gases on plane surfaces of glass, mica and platinum. Journal of the American Chemical society, 40(9), pp. 1361-1403. DOI:10.1021/ja02242a004
  15. Lee, C., Lee, S., Park, J., Park, C., Lee, S. J., Kim, S., An, B., Yun, S., Lee, S. & Choi, J. (2017). Removal of copper, nickel and chromium mixtures from metal plating wastewater by adsorption with modified carbon foam. Chemosphere, 166, pp. 203-211. DOI:10.1016/j.chemosphere.2016.09.093
  16. Lin, S. & Juang, R. (2002). Heavy metal removal from water by sorption using surfactant-modified montmorillonite. Journal of Hazardous Materials, 92(3), pp. 315-326. DOI:10.1016/S0304-3894(02)00026-2
  17. Liu, C., Wu, P., Zhu, Y. & Tran, L. (2016). Simultaneous adsorption of Cd2+ and BPA on amphoteric surfactant activated montmorillonite. Chemosphere, 144, pp. 1026-1032. DOI:10.1016/j.chemosphere.2015.09.063
  18. Long, H., Wu, P. & Zhu, N. (2013). Evaluation of Cs+ removal from aqueous solution by adsorption on ethylamine-modified montmorillonite. Chemical Engineering Journal, 225, pp. 237-244. DOI:10.1016/j.cej.2013.03.088
  19. Ma, J. & Zhu, L. (2006). Simultaneous sorption of phosphate and phenanthrene to inorgano–organo-bentonite from water. Journal of Hazardous Materials, 136(3), pp. 982-988. DOI:10.1016/j.jhazmat.2006.01.046
  20. Ma, J. & Zhu, L. (2007). Removal of phenols from water accompanied with synthesis of organobentonite in one-step process. Chemosphere, 68(10), pp. 1883-1888. DOI:10.1016/j.chemosphere.2007.03.002
  21. Ma, L., Chen, Q., Zhu, J., Xi, Y., He, H., Zhu, R., Tao, Q. & Ayoko, G. A. (2016). Adsorption of phenol and Cu(II) onto cationic and zwitterionic surfactant modified montmorillonite in single and binary systems. Chemical Engineering Journal, 283, pp. 880-888. DOI:10.1016/j.cej.2015.08.009
  22. Matthes, W., Madsen, F. T. & Kahr, G. (1999). Sorption of heavy-metal cations by Al and Zr-hydroxy-intercalated and pillared bentonite. Clays and Clay Minerals, 47(5), pp. 617-629. DOI:10.1346/CCMN.1999.0470508
  23. Meng, Z., Zhang, Y. & Zhang, Z. (2008). Simultaneous adsorption of phenol and cadmium on amphoteric modified soil. Journal of Hazardous Materials, 159(2), pp. 492-498. DOI:10.1016/j.jhazmat.2008.02.045
  24. Nourmoradi, H., Nikaeen, M. & Khiadani Hajian, M. (2012). Removal of benzene, toluene, ethylbenzene and xylene (BTEX) from aqueous solutions by montmorillonite modified with nonionic surfactant: Equilibrium, kinetic and thermodynamic study. Chemical Engineering Journal, 191, pp. 341-348. DOI:10.1016/j.cej.2012.03.029
  25. Pal, A., Jayamani, J. & Prasad, R. (2014). An urgent need to reassess the safe levels of copper in the drinking water: Lessons from studies on healthy animals harboring no genetic deficits. NeuroToxicology, 44, pp. 58-60. DOI:10.1016/j.neuro.2014.05.005
  26. Park, Y., Ayoko, G. A., Horváth, E., Kurdi, R., Kristof, J. & Frost, R. L. (2013). Structural characterisation and environmental application of organoclays for the removal of phenolic compounds. Journal of Colloid and Interface Science, 393, pp. 319-334. DOI:10.1016/j.jcis.2012.10.067
  27. Qu, Y., Qin, L., Liu, X. & Yang, Y. (2020). Reasonable design and sifting of microporous carbon nanosphere-based surface molecularly imprinted polymer for selective removal of phenol from wastewater. Chemosphere, 251, 126376. DOI:10.1016/j.chemosphere.2020.126376
  28. Redlich, O. & Peterson, D. L. (1959). A useful adsorption isotherm. Journal of physical chemistry, 63(6), 1024. DOI:10.1021/j150576a611
  29. Ren, S., Meng, Z., Sun, X., Lu, H., Zhang, M., Lahori, A. H. & Bu, S. (2020). Comparison of Cd2+ adsorption onto amphoteric, amphoteric-cationic and amphoteric-anionic modified magnetic bentonites. Chemosphere, 239, 124840. DOI:10.1016/j.chemosphere.2019.124840
  30. Senturk, H. B., Ozdes, D., Gundogdu, A., Duran, C. & Soylak, M. (2009). Removal of phenol from aqueous solutions by adsorption onto organomodified Tirebolu bentonite: Equilibrium, kinetic and thermodynamic study. Journal of Hazardous Materials, 172(1), pp. 353-362. DOI:10.1016/j.jhazmat.2009.07.019
  31. Taffarel, S. R. & Rubio, J. (2010). Adsorption of sodium dodecyl benzene sulfonate from aqueous solution using a modified natural zeolite with CTAB. Minerals Engineering, 23(10), pp. 771-779. DOI:10.1016/j.mineng.2010.05.018
  32. Tri, N. L. M., Thang, P. Q., Van Tan, L., Huong, P. T., Kim, J., Viet, N. M., Phuong, N. M. & Al Tahtamouni, T. M. (2020). Removal of phenolic compounds from wastewaters by using synthesized Fe-nano zeolite. Journal of Water Process Engineering, 33, 101070. DOI:10.1016/j.jwpe.2019.101070
  33. Veli, S. & Alyüz, B. (2007). Adsorption of copper and zinc from aqueous solutions by using natural clay. Journal of Hazardous Materials, 149(1), pp. 226-233. DOI:10.1016/j.jhazmat.2007.04.109
  34. Wang, G., Wang, X., Zhang, S., Ma, S., Wang, Y. & Qiu, J. (2020). Adsorption of heavy metal and organic pollutant by organo-montmorillonites in binary-component system. Journal of Porous Materials, 27(5), pp. 1515-1522. DOI:10.1007/s10934-020-00927-8
  35. Wang, G., Zhang, S., Hua, Y., Su, X., Ma, S., Wang, J., Tao, Q., Wang, Y. & Komarneni, S. (2017). Phenol and/or Zn2+ adsorption by single- or dual-cation organomontmorillonites. Applied Clay Science, 140, pp. 1-9. DOI:10.1016/j.clay.2017.01.023
  36. Yan, L., Shan, X., Wen, B. & Zhang, S. (2007). Effect of lead on the sorption of phenol onto montmorillonites and organo-montmorillonites. Journal of Colloid and Interface Science, 308(1), pp. 11-19. DOI:10.1016/j.jcis.2006.12.027
  37. Yang, G., Tang, L., Zeng, G., Cai, Y., Tang, J., Pang, Y., Zhou, Y., Liu, Y., Wang, J., Zhang, S. & Xiong, W. (2015). Simultaneous removal of lead and phenol contamination from water by nitrogen-functionalized magnetic ordered mesoporous carbon. Chemical Engineering Journal, 259, pp. 854-864. DOI:10.1016/j.cej.2014.08.081
  38. Yoo, J., Choi, J., Lee, T. & Park, J. (2004). Organobentonite for sorption and degradation of phenol in the presence of heavy metals. Water, Air, and Soil Pollution, 154(1), pp. 225-237. DOI:10.1023/B:WATE.0000022970.21712.64
  39. Yu, K., Xu, J., Jiang, X., Liu, C., McCall, W. & Lu, J. (2017). Stabilization of heavy metals in soil using two organo-bentonites. Chemosphere, 184, pp.884-891. DOI:10.1016/j.chemosphere.2017.06.040
  40. Zendelska, A., Golomeova, M., Golomeov, B. & Krstev, B. (2018). Removal of lead ions from acid aqueous solutions and acid mine drainage using zeolite bearing tuff. Archives of Environmental Protection, 44(1), pp. 87-96. DOI:10.24425/118185
  41. Zhu, R., Chen, Q., Zhou, Q., Xi, Y., Zhu, J. & He, H. (2016). Adsorbents based on montmorillonite for contaminant removal from water: A review. Applied Clay Science, 123, pp. 239-258. DOI:10.1016/j.clay.2015.12.024
  42. Andronico, M. & Bajda, T. (2019). Modification of Bentonite with Cationic and Nonionic Surfactants: Structural and Textural Features. Materials, 12(22), 3772. DOI:10.3390/ma12223772
  43. Banat, F. A., Al-Bashir, B., Al-Asheh, S. & Hayajneh, O. (2000). Adsorption of phenol by bentonite. Environmental Pollution, 107(3), pp. 391-398. DOI:10.1016/S0269-7491(99)00173-6
  44. Bhattacharyya, K. G. & Gupta, S. S. (2008). Adsorption of a few heavy metals on natural and modified kaolinite and montmorillonite: A review. Advances in Colloid and Interface Science, 140(2), pp. 114-131. DOI:10.1016/j.cis.2007.12.008
  45. Cao, L., Li, Z., Xiang, S., Huang, Z., Ruan, R. & Liu, Y. (2019). Preparation and characteristics of bentonite–zeolite adsorbent and its application in swine wastewater. Bioresource Technology, 284, pp. 448-455. DOI:10.1016/j.biortech.2019.03.043
  46. Chen, H., Zhou, W., Zhu, K., Zhan, H. & Jiang, M. (2004). Sorption of ionizable organic compounds on HDTMA-modified loess soil. Science of The Total Environment, 326(1), pp. 217-223. DOI:10.1016/j.scitotenv.2003.12.011
  47. Chen, Y., Zhang, X., Wang, L., Cheng, X. & Shang, Q. (2020). Rapid removal of phenol/antibiotics in water by Fe-(8-hydroxyquinoline-7-carboxylic)/TiO2 flower composite: Adsorption combined with photocatalysis. Chemical Engineering Journal, 402, 126260. DOI:10.1016/j.cej.2020.126260
  48. Chu, Y., Khan, M. A., Xia, M., Lei, W., Wang, F., Zhu, S. & Yan, X. (2020). Synthesis and micro-mechanistic studies of histidine modified montmorillonite for lead(II) and copper(II) adsorption from wastewater. Chemical Engineering Research and Design, 157, pp. 142-152. DOI:10.1016/j.cherd.2020.02.020
  49. Díaz-Nava, M. C., Olguín, M. T. & Solache-Ríos, M. (2012). Adsorption of phenol onto surfactants modified bentonite. Journal of Inclusion Phenomena and Macrocyclic Chemistry, 74(1), 67-75. DOI:10.1007/s10847-011-0084-6
  50. Fan, H., Zhou, L., Jiang, X., Huang, Q. & Lang, W. (2014). Adsorption of Cu2+ and methylene blue on dodecyl sulfobetaine surfactant-modified montmorillonite. Applied Clay Science, 95, pp. 150-158. DOI:10.1016/j.clay.2014.04.001
  51. Freundlich, H. (1906). Over the adsorption in solution. The Journal of Physical Chemistry A, 57(385471), pp. 1100-1107. DOI:10.1515/zpch-1907-5723
  52. Griffin, R. A. & Shimp, N. F. (1976). Effect of pH on exchange-adsorption or precipitation of lead from landfill leachates by clay minerals. Environmental science & technology, 10(13), pp. 1256-1261. DOI:10.1021/es60123a003
  53. He, Y., Chen, Y., Zhang, K., Ye, W. & Wu, D. (2019). Removal of chromium and strontium from aqueous solutions by adsorption on laterite. Archives of Environmental Protection, 45(3), pp. 11-20. DOI:10.24425/aep.2019.128636
  54. Kong, Y., Wang, L., Ge, Y., Su, H. & Li, Z. (2019). Lignin xanthate resin–bentonite clay composite as a highly effective and low-cost adsorbent for the removal of doxycycline hydrochloride antibiotic and mercury ions in water. Journal of Hazardous Materials, 368, pp. 33-41. DOI:10.1016/j.jhazmat.2019.01.026
  55. Langmuir, I. (1918). The adsorption of gases on plane surfaces of glass, mica and platinum. Journal of the American Chemical society, 40(9), pp. 1361-1403. DOI:10.1021/ja02242a004
  56. Lee, C., Lee, S., Park, J., Park, C., Lee, S. J., Kim, S., An, B., Yun, S., Lee, S. & Choi, J. (2017). Removal of copper, nickel and chromium mixtures from metal plating wastewater by adsorption with modified carbon foam. Chemosphere, 166, pp. 203-211. DOI:10.1016/j.chemosphere.2016.09.093
  57. Lin, S. & Juang, R. (2002). Heavy metal removal from water by sorption using surfactant-modified montmorillonite. Journal of Hazardous Materials, 92(3), pp. 315-326. DOI:10.1016/S0304-3894(02)00026-2
  58. Liu, C., Wu, P., Zhu, Y. & Tran, L. (2016). Simultaneous adsorption of Cd2+ and BPA on amphoteric surfactant activated montmorillonite. Chemosphere, 144, pp. 1026-1032. DOI:10.1016/j.chemosphere.2015.09.063
  59. Long, H., Wu, P. & Zhu, N. (2013). Evaluation of Cs+ removal from aqueous solution by adsorption on ethylamine-modified montmorillonite. Chemical Engineering Journal, 225, pp. 237-244. DOI:10.1016/j.cej.2013.03.088
  60. Ma, J. & Zhu, L. (2006). Simultaneous sorption of phosphate and phenanthrene to inorgano–organo-bentonite from water. Journal of Hazardous Materials, 136(3), pp. 982-988. DOI:10.1016/j.jhazmat.2006.01.046
  61. Ma, J. & Zhu, L. (2007). Removal of phenols from water accompanied with synthesis of organobentonite in one-step process. Chemosphere, 68(10), pp. 1883-1888. DOI:10.1016/j.chemosphere.2007.03.002
  62. Ma, L., Chen, Q., Zhu, J., Xi, Y., He, H., Zhu, R., Tao, Q. & Ayoko, G. A. (2016). Adsorption of phenol and Cu(II) onto cationic and zwitterionic surfactant modified montmorillonite in single and binary systems. Chemical Engineering Journal, 283, pp. 880-888. DOI:10.1016/j.cej.2015.08.009
  63. Matthes, W., Madsen, F. T. & Kahr, G. (1999). Sorption of heavy-metal cations by Al and Zr-hydroxy-intercalated and pillared bentonite. Clays and Clay Minerals, 47(5), pp. 617-629. DOI:10.1346/CCMN.1999.0470508
  64. Meng, Z., Zhang, Y. & Zhang, Z. (2008). Simultaneous adsorption of phenol and cadmium on amphoteric modified soil. Journal of Hazardous Materials, 159(2), pp. 492-498. DOI:10.1016/j.jhazmat.2008.02.045
  65. Nourmoradi, H., Nikaeen, M. & Khiadani Hajian, M. (2012). Removal of benzene, toluene, ethylbenzene and xylene (BTEX) from aqueous solutions by montmorillonite modified with nonionic surfactant: Equilibrium, kinetic and thermodynamic study. Chemical Engineering Journal, 191, pp. 341-348. DOI:10.1016/j.cej.2012.03.029
  66. Pal, A., Jayamani, J. & Prasad, R. (2014). An urgent need to reassess the safe levels of copper in the drinking water: Lessons from studies on healthy animals harboring no genetic deficits. NeuroToxicology, 44, pp. 58-60. DOI:10.1016/j.neuro.2014.05.005
  67. Park, Y., Ayoko, G. A., Horváth, E., Kurdi, R., Kristof, J. & Frost, R. L. (2013). Structural characterisation and environmental application of organoclays for the removal of phenolic compounds. Journal of Colloid and Interface Science, 393, pp. 319-334. DOI:10.1016/j.jcis.2012.10.067
  68. Qu, Y., Qin, L., Liu, X. & Yang, Y. (2020). Reasonable design and sifting of microporous carbon nanosphere-based surface molecularly imprinted polymer for selective removal of phenol from wastewater. Chemosphere, 251, 126376. DOI:10.1016/j.chemosphere.2020.126376
  69. Redlich, O. & Peterson, D. L. (1959). A useful adsorption isotherm. Journal of physical chemistry, 63(6), 1024. DOI:10.1021/j150576a611
  70. Ren, S., Meng, Z., Sun, X., Lu, H., Zhang, M., Lahori, A. H. & Bu, S. (2020). Comparison of Cd2+ adsorption onto amphoteric, amphoteric-cationic and amphoteric-anionic modified magnetic bentonites. Chemosphere, 239, 124840. DOI:10.1016/j.chemosphere.2019.124840
  71. Senturk, H. B., Ozdes, D., Gundogdu, A., Duran, C. & Soylak, M. (2009). Removal of phenol from aqueous solutions by adsorption onto organomodified Tirebolu bentonite: Equilibrium, kinetic and thermodynamic study. Journal of Hazardous Materials, 172(1), pp. 353-362. DOI:10.1016/j.jhazmat.2009.07.019
  72. Taffarel, S. R. & Rubio, J. (2010). Adsorption of sodium dodecyl benzene sulfonate from aqueous solution using a modified natural zeolite with CTAB. Minerals Engineering, 23(10), pp. 771-779. DOI:10.1016/j.mineng.2010.05.018
  73. Tri, N. L. M., Thang, P. Q., Van Tan, L., Huong, P. T., Kim, J., Viet, N. M., Phuong, N. M. & Al Tahtamouni, T. M. (2020). Removal of phenolic compounds from wastewaters by using synthesized Fe-nano zeolite. Journal of Water Process Engineering, 33, 101070. DOI:10.1016/j.jwpe.2019.101070
  74. Veli, S. & Alyüz, B. (2007). Adsorption of copper and zinc from aqueous solutions by using natural clay. Journal of Hazardous Materials, 149(1), pp. 226-233. DOI:10.1016/j.jhazmat.2007.04.109
  75. Wang, G., Wang, X., Zhang, S., Ma, S., Wang, Y. & Qiu, J. (2020). Adsorption of heavy metal and organic pollutant by organo-montmorillonites in binary-component system. Journal of Porous Materials, 27(5), pp. 1515-1522. DOI:10.1007/s10934-020-00927-8
  76. Wang, G., Zhang, S., Hua, Y., Su, X., Ma, S., Wang, J., Tao, Q., Wang, Y. & Komarneni, S. (2017). Phenol and/or Zn2+ adsorption by single- or dual-cation organomontmorillonites. Applied Clay Science, 140, pp. 1-9. DOI:10.1016/j.clay.2017.01.023
  77. Yan, L., Shan, X., Wen, B. & Zhang, S. (2007). Effect of lead on the sorption of phenol onto montmorillonites and organo-montmorillonites. Journal of Colloid and Interface Science, 308(1), pp. 11-19. DOI:10.1016/j.jcis.2006.12.027
  78. Yang, G., Tang, L., Zeng, G., Cai, Y., Tang, J., Pang, Y., Zhou, Y., Liu, Y., Wang, J., Zhang, S. & Xiong, W. (2015). Simultaneous removal of lead and phenol contamination from water by nitrogen-functionalized magnetic ordered mesoporous carbon. Chemical Engineering Journal, 259, pp. 854-864. DOI:10.1016/j.cej.2014.08.081
  79. Yoo, J., Choi, J., Lee, T. & Park, J. (2004). Organobentonite for sorption and degradation of phenol in the presence of heavy metals. Water, Air, and Soil Pollution, 154(1), pp. 225-237. DOI:10.1023/B:WATE.0000022970.21712.64
  80. Yu, K., Xu, J., Jiang, X., Liu, C., McCall, W. & Lu, J. (2017). Stabilization of heavy metals in soil using two organo-bentonites. Chemosphere, 184, pp.884-891. DOI:10.1016/j.chemosphere.2017.06.040
  81. Zendelska, A., Golomeova, M., Golomeov, B. & Krstev, B. (2018). Removal of lead ions from acid aqueous solutions and acid mine drainage using zeolite bearing tuff. Archives of Environmental Protection, 44(1), pp. 87-96. DOI:10.24425/118185
  82. Zhu, R., Chen, Q., Zhou, Q., Xi, Y., Zhu, J. & He, H. (2016). Adsorbents based on montmorillonite for contaminant removal from water: A review. Applied Clay Science, 123, pp. 239-258. DOI:10.1016/j.clay.2015.12.024
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Authors and Affiliations

Xiangyang Hu
1
Bao Wang
2
ORCID: ORCID
Gengsheng Yan
1
Bizhou Ge
2

  1. PowerChina Northwest Engineering Corporation Limited, China
  2. Xi’an University of Architecture and Technology, China
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Abstract

The paper presents a microscopic analysis of the surface and fracture of aluminium castings produced using the lost-wax method for patterns made of a composite material, i.e. polyethylene with the addition of bentonite. Castings are made of AlSi7 aluminium alloy (silumin) in a plaster mould. A new type of polymer waxes enriched with bentonite was used to obtain new composites, minimizing the defects caused by the casting production process. The castings were made in the centrifugal casting process. The prepared plaster moulds were removed from the furnace and poured with liquid aluminium alloy (AlSi7) at 750°C. The surface and fracture of the castings was analysed using an optical digital microscope type VHX-7000 manufactured by KEYENCE. It has been proven that the studied castings feature surface defects (raw surface defects) in the form of high roughness and the presence of bentonite inclusions classified as casting contamination. During the tests, shape defects related to mechanical damage were also detected.
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Bibliography

[1] Kozakowski, S. (2001). Study of castings. Warsaw: Biuro Gamma. (in Polish)
[2] Sozański, L. (2004). Visual examination of castings surface discontinuities according to European standards. Archives of Foundry. 4(11). 196-199. (in Polish)
[3] Sozański, L. (2006). Possibilities of assessment of surface discontinuities of castings. Archiwum Odlewnictwa. 6(2), 331-336. (in Polish)
[4] PN EN 1559-1 Founding – Technical delivery conditions – General provisions. (in Polish)
[5] PN EN 1371-2 Founding. Penetrant testing. Part 2: Castings made using the lost-wax method. (in Polish)
[6] PN EN 1370 Founding – Surface roughness testing using visual-tactile standards. (in Polish)
[7] Kuchariková, L., Tillová, E., Samardžiová, M. et al., (2019). Quality assessment of Al castings produced in sand molds using image and CT analyses. Journal of Materials Engineering and Performance. 28, 3966-3973. https://doi.org/10.1007/s11665-019-04040-z.
[8] Sika, R., Rogalewicz, M., Popielarski, P., Czarnecka-Komorowska, D., Przestacki, D., Gawdzińska, K. & Szymański, P. (2020). Decision support system in the field of defects assessment in the metal matrix composites castings. Materials. 13(16), 3552. https://doi.org/10.3390/ma13163552
[9] Tupaj, M., Orłowicz, A.W., Mróz, M., Trytek,. A., & Markowska, O. (2016). The effect of cooling rate on properties of intermetallic phase in a complex Al-Si alloy. Archives of Foundry Engineering. 16(3), 125-128. DOI: 10.1515/afe-2016-0063
[10] Gawdzińska, K., Chybowski, L., Bejger J.A. & Krile, S. (2016). Determination of technological parameters of saturated composites based on SiC by means of a model liquid. Metalurgija. 55(4) 659-662. https://hrcak.srce.hr/157391
[11] Aziz, M.N., Munyensanga, P. & Widyanto, S.A. (2018). Application of lost wax casting for manufacturing of orthopedic screw: A review. Procedia CIRP. 78, 149-154.
[12] Zych, J., Kolczyk, J., & Snopkiewicz, T. (2012). Investigations of properties of wax mixtures used in the investment casting technology, New investigation methods. Archives of Foundry Engineering. 12(spec.1), 199-204. ISSN (1897-3310)
[13] Wen, J., Xie, Z., Cao, W. & Yang, X. (2016). Effects of different backbone binders on the characteristics of zirconia parts using wax-based binder system via ceramic injection molding. Journal of Advanced Ceramics. 5(4), 321-328. https://doi.org/10.1007/s40145-016-0205-1
[14] Czarnecka-Komorowska, D., Grześkowiak, K., Popielarski, P., Barczewski, M., Gawdzińska, K. & Popławski, M. (2020). Polyethylene wax modified by organoclay bentonite used in the lost-wax casting process: processing−structure−property relationships. Materials. 13(2255), 1-22. https://doi.org/10.3390/ma13102255.
[15] Naplocha, K. & Granat, K. (2008). Dry sliding wear of Al/Saffil/C hybrid metal matrix composites. Wear. 265(11-12), 1734-1740. https://doi.org/10.1016/j.wear.2008.04.006
[16] Olszówka-Myalska, A., Godzierz, M., Myalski, J. & Wrześniowski, P. (2019). Magnesium matrix composites with open-celled glassy carbon foam obtained using the infiltration method. Metals. 9(622), 1-14. DOI: 10.3390/met9060622
[17] Grzeskowiak, K., Czarnecka-Komorowska, D., Sytek K. & Wojciechowski, M. (2015). Influence of waxes remelting used in investment casting on their thermal properties and linear shrinkage. Metalurgija. 54(2), 350-352. https://hrcak.srce.hr/128959
[18] Trytek, A., Orłowicz, A.W., Tupaj, M., Mróz, M., Markowska, O., Bąk, G. & Abram, T. (2016). The effect of a thin459 wall casting mould cavity filling conditions on the casting surface quality. Archives of Foundry Engineering. 16(4), 222-226. DOI: 10.1515/afe-2016-0113
[19] Dolata, A.J., Dyzia, M., Putyra, P. & Jaworska, L. (2016). Cast hybrid composites designated for air compressor 549 pistons. Archives of Metallurgy and Materials. 61(2), 705-708. DOI: 10.1515/amm-2016-0120
[20] Staude, M. (2021). Porosity assessment of suspension and saturated composite castings with the use of microscopic examinations. Scientific Journals of the Maritime University of Szczecin. 67(139), 53-57.
[21] Skołek, E., Giętka, T., Świątnicki, W. & Myszka, D. (2017). The comparative study of the microstructure and phase composition of nanoausferritic ductile iron alloy using SEM, TEM, magnetometer, and X-ray diffraction methods. Acta Physica Polonica A. 5(131), 1319-1323, DOI: 10.12693/APhysPolA.131.1319
[22] Polish Standard PN-85/H-83105. Castings. Division and terminology of defects. (in Polish)

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Authors and Affiliations

D. Czarnecka-Komorowska
1
ORCID: ORCID
K. Gawdzińska
2
ORCID: ORCID
P. Popielarski
1
ORCID: ORCID

  1. Poznań University of Technology, Poland
  2. Maritime University of Szczecin, Poland
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Abstract

This study explores the influence of alkali activators on the initiation of polymerization reaction of alumino-silicate minerals present in class-F fly ash material. Different types of fly ash aggregates were produced with silicate rich binders (bentonite and metakaolin) and the effect of alkali activators on the strength gain properties were analyzed. A comprehensive examination on its physical and mechanical properties of the various artificial fly ash aggregates has been carried out systematically. A pelletizer machine was fabricated in this study to produce aggregate pellets from fly ash. The efficiency and strength of pellets was improved by mixing fly ash with different binder materials such as ground granulated blast furnace slag (GGBS), metakaolin and bentonite. Further, the activation of fly ash binders was done using sodium hydroxide for improving its binding properties. Concrete mixes were designed and prepared with the different fly ash based aggregates containing different ingredients. Hardened concrete specimens after sufficient curing was tested for assessing the mechanical properties of different types concrete mixes. Test results indicated that fly ash -GGBS aggregates (30S2‒100) with alkali activator at 10M exhibited highest crushing strength containing of 22.81 MPa. Similarly, the concrete mix with 20% fly ash-GGBS based aggregate reported a highest compressive strength of 31.98 MPa. The fly ash based aggregates containing different binders was found to possess adequate engineering properties which can be suggested for moderate construction works.

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Authors and Affiliations

P. Gomathi
A. Sivakumar
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Abstract

In recent years, there has been a marked increase in the amount of municipal waste generated in Poland. In 2020, 21.6% of all municipal waste was subjected to a thermal treatment process. Consequently, the amount of ashes generated is significant. Due to their properties, it is difficult to utilize this type of waste within concrete production technology. One of the waste utilization methods is to add it to hardening slurries used in, among others, cut-off walls. The article assesses the possibility of using ashes from municipal waste incineration as an additive to hardening slurries. It also discusses the technological properties of hardening slurries with the addition of the ashes in question. The experiment showed that it is possible to compose a hardening slurry based on tested ashes with technological properties suitable for use as a cut-off wall. Further research directions were proposed.
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Bibliography

  1. Almahdawi, F.H.M.; Al-Yaseri, A.Z. & Jasim, N. (2014). Apparent viscosity direct from Marsh funnel test. Iraqi Journal of Chemical and Petroleum Engineering, 15(1), pp. 51-57, ISSN: 1997-4884
  2. Alwaeli, M.; Alshawaf, M. & Klasik, M. (2022). Recycling of selected fraction of municipal solid waste as artificial soil substrate in support of the circular economy. Archives of Environmental Protection, 48(4), pp. 68–77. DOI:10.24425/aep.2022.143710
  3. Borys, M. (2012). Hardening slurry cut-off walls in dyke bodies and bases. Wiadomości melioracyjne i łąkarskie, 55(2), pp. 89-95. (in Polish).
  4. Borys, M.; Rycharska, J. (2006). Parameters of hardening slurries used for the construction of cut-off walls in dykes. Woda-Środowisko-Obszary Wiejskie, 6(1), pp.47-56. (in Polish)
  5. Chomkhamsri, K. & Pelletier, N. (2011). Analysis of existing environmental footprint methodologies for products and organizations: recommendations, rationale, and alignment. Institute for Environment and Sustainability, pp. 1-61.
  6. Domańska, W.; Bochenek, D.; Dawgiałło, U.; Gorzkowska, E.; Hejne, J.; Kiełczykowska, A.; Kruszewska, D.; Nieszałą, A.; Nowakowska, B.; Sulik, J.; Wichniewicz, A.; Wrzosek, A. (2022). Environment 2022. Statistics Poland. Warsaw, 157–158p.
  7. Falacinski, 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, pp. 47-61.DOI: 10.1515/heem-2016-0004
  8. Falaciński, P. (2012). Possible applications of hardening slurries with fluidal ashes in environment protection structures. Archives of Environmental Protection 38, pp. 91-104. DOI:10.2478/v10265-012-0031-7
  9. Falaciński, P.; Kledyński, Z. (2006). Influence of aggressive liquids on hydraulic conductivity of hardening slurries with the addition of different fluidal fly ashes. Environmental Engineering: Proceedings of the 2nd National Congress on Environmental Engineering, 4-8 September 2005. CRC Press, pp. 295-300.
  10. Ferreira, C.; Ribeiro, A.; Ottosen, L. (2003). Possible applications for municipal solid waste fly ash. Journal of Hazardous Materials, 96(2-3), pp. 201-216.
  11. Garvin, S.L.; Hayles, C.S. (1999). The chemical compatibility of cement–bentonite cut-off wall material. Construction and Building Materials, 13(6), pp. 329-341.
  12. Jefferis, S. (2012). Cement-bentonite slurry systems. In Grouting and Deep Mixing 2012, pp.1-24.
  13. Jefferis, S. (2013). Grouts and slurries. In Construction Materials Reference Book. Routledge, pp. 173-202.
  14. Jefferis, S.A. (2008). Reactive transport in cut-off walls and implications for wall durability. In GeoCongress 2008: Geotechnics of Waste Management and Remediation, pp. 652-659.
  15. Kledynski, Z.; Machowska, A. (2013). Hardening slurries with ground granulated blast furnace slag activated with fluidal fly ash from lignite combustion. Przemysł Chemiczny 92(4), pp.490-497. (in Polish)
  16. Kledyński, Z. (1989). The use of statistical planning of experiments in the search for a frost resistant hardening slurry. Gospodarka Wodna, 9, pp. 181-184. (in Polish)
  17. Kledyński, Z. (2000). Corrosion resistance of hardening slurries in environmental facilities. Prace Naukowe Politechniki Warszawskiej. Inżynieria Środowiska, 33, pp. 3-101. (in Polish)
  18. Kledyński, Z.; Rafalski, L. (2009). Hardening slurries. Komitet Inżynierii Lądowej i Wodnej Polskiej Akademii Nauk Instytut Podstawowych Problemów Technicznych. Studia z Zakresu Inżynierii, 66. Warszawa. pp.1-234. (in Polish)
  19. Kledyński, Z.; Falaciński, P.; Machowska, A.; Dyczek, J. (2016). Utilisation of CFBC fly ash in hardening slurries for flood-protecting dikes. Archives of Civil Engineering, 62, pp. 75-88.
  20. Kledyński, Z.; Falaciński, P.; Machowska, A.; Szarek, Ł.; Krysiak, Ł. (2021). Hardening Slurries with Fluidized-Bed Combustion By-Products and Their Potential Significance in Terms of Circular Economy. Materials, 14(9). DOI: 10.3390/ma14092104
  21. Kumar, A.; Mittal, A. (2019). Utilization of municipal solid waste ash for stabilization of cohesive soil. In Environmental Geotechnology: Proceedings of EGRWSE 2018, Springer. Singapore, pp .133-139.
  22. Lam, C.H.K.; Barford, J.P.; McKay, G. (2011). Utilization of municipal solid waste incineration ash in Portland cement clinker. Clean technologies and environmental policy, 13, pp. 607-615.
  23. Liang, S.; Chen, J.; Guo, M.; Feng, D.; Liu, L.; Qi, T. (2020). Utilization of pretreated municipal solid waste incineration fly ash for cement-stabilized soil. Waste Management, 105:, pp. 425-432. DOI: 10.1016/j.wasman.2020.02.017
  24. Marsh, H.N. (1931). Properties and treatment of rotary mud. Transactions of the AIME, 92, pp. 234-251.
  25. Mewis, J. (1979). Thixotropy-a general review. Journal of Non-Newtonian Fluid Mechanics, 6, pp. 1-20.
  26. Opdyke, S.M.; Evans, J.C. (2005). Slag-Cement-Bentonite Slurry Walls. Journal of Geotechnical and Geoenvironmental Engineering, 131, pp. 673-681.
  27. Orr, J.; Gibbons, O.; Arnold, W. (2020). A brief guide to calculating embodied carbon.
  28. Pawnuk, M.; Szulczyński, B.; den Boer, E.; Sówka, I. (2022). Preliminary analysis of the state of municipal waste management technology in Poland along with the identification of waste treatment processes in terms of odor emissions. Archives of Environmental Protection, 48(3), pp. 3-20. DOI: 10.24425/aep.2022.142685
  29. Peters, G.P. (2010). Carbon footprints and embodied carbon at multiple scales. Current Opinion in Environmental Sustainability, 2, pp. 245-250.
  30. Primus, A.; Chmielniak, T.; Rosik-Dulewska, C. (2021). Concepts of energy use of municipal solid waste. Archives of Environmental Protection, 47(2), pp. 70-80. DOI: 10.24425/aep.2021.137279
  31. Rafalski, L. (1995). Właściwości i zastosowanie zawiesin twardniejących. Instytut Badawczy Dróg i Mostów.
  32. Ruffing, D.; Evans, J. (2019). Soil Mixing and Slurry Trench Cutoff Walls for Coal Combustion Residue Sites. 2019 World of Coal Ash.
  33. Siddique, R. (2010)a. Use of municipal solid waste ash in concrete. Resources. Conservation and Recycling, 55, pp. 83-91.
  34. Siddique, R. (2010)b. Utilization of municipal solid waste (MSW) ash in cement and mortar. Resources, Conservation and Recycling, 54, pp. 1037-1047.
  35. Stanisz, A. (2007). Przystępny kurs statystyki: z zastosowaniem STATISTICA PL na przykładach z medycyny. Analizy wielowymiarowe. StatSoft.
  36. Szarek, Ł. (2019). The influence of addition fly ash from thermal treatment of municipal sewage sludge on selected hardening slurries properties. In Monitoring and Safety of Hydrotechnical Constructions, pp.329-340. (in Polish)
  37. 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
  38. Talefirouz, D.; Çokça, E.; Omer, J. (2016). Use of granulated blast furnace slag and lime in cement-bentonite slurry wall construction. International journal of geotechnical engineering, 10, pp. 81-85.
  39. Uliasz-Bocheńczyk, A.; Deja, J.; Mokrzycki, E. (2021). The use of alternative fuels in the cement industry as part of circular economy. Archives of Environmental Protection, 47(4), pp. 109-117. DOI: 10.24425/aep.2021.139507
  40. Wiedmann, T.; Minx, J. (2008). A definition of ‘carbon footprint.’ Ecological economics research trends, 1, pp. 1-11.
  41. Wielgosiński, G. (2016). Spalarnie odpadów komunalnych w perspektywie 2020 r. Przegląd Komunalny, pp. 30-32.
  42. Wojtkowska, M.; Falaciński, P.; Kosiorek, A. (2016). The release of heavy metals from hardening slurries with addition of selected combustion by-products. Inżynieria i Ochrona Środowiska, 19, pp. 479-491. (in Polish)
  43. EN 450-1:2012 Fly ash for concrete. Definition, specifications and conformity criteria.
  44. ISO/TS 14067:2013 Greenhouse gases — Carbon footprint of products — Requirements and guidelines for quantification and communication. .
  45. Regulation of the Minister of Climate of 2 January 2020 on the waste catalogue (Journal of Laws from 2020, item. 10 - Dz.U. 2020 poz. 10). (in Polish)
  46. Waste Act of 14 December 2012 r. (Journal of Laws from 2013, item. 21 - Dz.U. 2013 poz. 21). (in Polish)
  47. PN-EN 196-2:2013-11 Methods of testing cement -- Part 2: Chemical analysis of cement. (in Polish)
  48. PN EN 451-2:2017-06 Method of testing fly ash - Part 2: Determination of fineness by wet sieving. (in Polish)
  49. BN-90/1785-01:1990. Drilling mud. Field test methods. (in Polish)
  50. PN-85/G-02320:1985. Drilling. Cements and grouts for cementing in boreholes. (in Polish)
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Authors and Affiliations

Łukasz Szarek
1
ORCID: ORCID
Paweł Falaciński
1
ORCID: ORCID
Piotr Drużyński
1

  1. Faculty of Building Services, Hydro and Environmental Engineering,Warsaw University of Technology, Poland
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Abstract

The process of sorption of chromium(III) ions with a stationary sorbent layer of bentonite clays was investigated. The main advantages of using bentonites in water purification technologies are described: powerful geological reserves, cheap process of rock extraction, easy preparation for transportation and use, possibility of using waste sorbents in other technol-ogies that is why there is no need in costly regeneration. The influence of various factors (process duration, an adsorbent layer) on the degree of wastewater purification from chromium ions, the effect of pumping speed on the dynamic capacity of the sorbent was studied and the effective volume was determined. The adsorption efficacy increases with the increase of the adsorbent layer, what can be explained by the development of the active sorption surface. As the initial concentration of chromium ions increases, the time of appearance of the first traces of the contaminant at the exit of the column increases, as well as the total time to channeling. The results of the studies indicate a higher adsorption capacity of modified bentonite with respect to Cr3+ ions compared to its natural formula. The cleaning efficacy of the solution with a concentration of chromium ions of 0.5 g∙dm–3 is increased by 5% when using 15 g of modified bentonite and 6,5% in the case one uses 20 g compared to the natural form.
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Bibliography

ANNAN E., AGYEI-TUFFOUR B., BENSAH Y.D., KONADU D.S., YAYA A., ONWONA-AGYEMAN B., NYANKSON E. 2018. Application of clay ceramics and nanotechnology in water treatment: A review. Cogent Engineering. Vol. 5 (1) p. 1–35. DOI 10.1080/23311916.2018.1476017.
ILANGO A.K., NATRAYASAMY V. 2018. Hydrothermal fabrication of zirconium oxyhydroxide capped chitosan/kaolin framework for highly selective nitrate and phosphate retention. Industrial & Engineering Chemistry Research. Vol. 57 (43) p. 14470–14481. DOI 10.1021/acs.iecr.8b01859.
KASHIF UDDIN M. 2017. A review on the adsorption of heavy metals by clay minerals, with special focus on the past decade. Chemical Engineering Journal. Vol. 308 p. 438–462. DOI 10.1016/j.cej.2016.09.029.
KOŁODYŃSKA D., GĘCA M., HUBICKI Z. 2017. Zastosowanie sorbentów naturalnych w procesie usuwania jonów metali ciężkich [Use of natural sorbents for removal of heavy metal ions]. Przemysł Chemiczny. T. 96. Nr 5 p. 1139–1145. DOI 10.15199/62.2017.5.33.
KONEFAŁ M., PETRUS R., WARCHOŁ J.K. 2015. Equilibrium study of heavy metals adsorption on kaolin. Industrial and Engineering Chemistry Research. Vol 54, 27 p. 6975–6984. DOI 10.1021/acs.iecr.5b00880.
MALOVANYY M., SAKALOVA H., MALOVANYY M., VASYLINYCH T., PALAMARCHUK O., SEMCHUK J. 2019. Treatment of effluents from ions of heavy metals as display of environmentally responsible activity of modern businessman. Journal of Ecological Engineering. Vol. 4 (20) p. 167–176. DOI 10.12911/ 22998993/102841.
MENG F. YUAN G., WEI J., BI D., WANG H. 2017. Leonardite-derived humic substances are great adsorbents for cadmium. Environmental Science and Pollution Research. Vol. 24 (29) p. 23006–23014. DOI 10.1007/s11356-017-9947-8.
PALAMAR V., MARUKHLENKO M., MOKROUSOVA. O. 2015. Zastosuvannya khrommodyfikovanykh dyspersiy montmorylonitu dlya stabilizatsiyi kolahenovoyi struktury dermy [Chromium-modified montmorillonite dispersions in stabiblizing derma collagen structure]. Eastern-European Journal of Enterprise Technologies. Vol. 6(75) р. 36–41. DOI 10.15587/1729-4061.2015.44238.
PALAMARCHUK O. 2011. Ekolohichna vidpovidal’nist’ yak osnova funktsionuvannya suchasnoho suspil’stva [Environmental responsibility as the basis for the functioning of modern society]. Aktualni problemy psykholohii : zb. nauk. pr. In-tu psykholohii im. H. S. Kostiuka NAPN Ukrainy. Zhytomyr: Vyd-vo ZhDU im. I. Franka. T. 7. Ekolohichna psykholohiia. Vyp. 26 р. 401–411.
PETRUS R., WARCHOŁ J.K. 2005. Heavy metal removal by clinoptilolite. An equilibrium study in multi-component systems. Water Research. Vol. 39 (5) p. 819–830. DOI 10.1016/ j.watres.2004.12.003.
PETRUSHKA I. YATCHYSHYN YU., PETRUSHKA K. 2014. Intensyfikatsiya sorbtsiyi tseziyu kompleksnymy pryrodnymy sorbentamy z ridkykh radioaktyvnykh seredovyshch [Cesium sorption intensification by complex natural sorbents from liquid radioactive media]. Eastern-European Journal of Enterprise Technologies. Vol. 5. 10(71) p. 47–50. DOI 10.15587/1729-4061.2014.28066.
QIN L. YAN L., CHEN J., LIU T., YU H., DU B. 2016. Enhanced removal of Pb2+, Cu2+, and Cd2+ by amino-functionalized magnetite/kaolin clay. Industrial & Engineering Chemistry Research. Vol. 55 (27) p. 7344–7354. DOI 10.1021/acs.iecr.6b00657.
REPO E. WARCHOL J., BHATNAGAR A., MUDHOO A., SILLANPАА M. 2013. Aminopolycarboxylic acid functionalized adsorbents for heavy metals removal from water. Water Research. Vol. 47. Iss. 14 p. 4812–4832 DOI 10.1016/j.watres.2013.06.020
REPO E. PETRUS R., SILLANPАА M., WARCHOL J. 2011. Equili¬brium studies on the adsorption of Co(II) and Ni(II) by modified silica gels: One-component and binary systems. Chemical Engineering Journal. Vol. 172. Iss. 1 p. 376–385. DOI 10.1016/j.cej.2011.06.019
REPO E. WARCHOL J., SILLANPАА M. 2017. Metal recovery and preconcentration by aminopolycarboxylic acid modified silica surfaces. Journal of Sustainable Development of Energy, Water and Environment Systems. Vol. 5. Iss. 1 p. 89–100. DOI 10.13044/j.sdewes.d5.0135.
SABADASH V. GUMNITSKYY JA., MYLIANYK O., ROMANIUK L. 2017. Concurrent sorption of copper and chromium cations by natural zeolite. Environmental Problems. Vol. 2. Iss. 1 p. 159–162.
SAKALOVA Н., VASYLINYCZ T., KOVAL N., KASHCHEI V. 2017. Investigation of the method of chemical desorption for extraction of nikel ions(II) from bentonite clays. Environmental Problems. Vol. 2. Iss. 4 p. 187–190.
SAKALOVA Н., PALAMARCHUK O., VASYLINYCZ T., PETRUSHKA K., ZAHARKO JA., STOKALYUK O. 2019. Socio-psychological essence of attractiveness for the subjects of entrepreneurial activities of adsorption extraction of nickel ions(II) by bentonite clays. Environmental Problems. Vol. 4. Iss. 2 p. 68–74. DOI 10.23939/ep2019.02.068.
SATHVIKA T., MANASI, RAJESH V., RAJESH N. 2015. Prospective application of Aspergillus species immobilized in sodium montmorillonite to remove toxic hexavalent chromium from wastewater. RSC Advances. Vol. 5 (129) p. 107031–107044. DOI 10.1039/C5RA22778J.
VASYLECHKO V., GRYSHCHOUK G., KUZMA YU., ZAKORDONSKIY V., VASYLECHKO L., LEBEDYNETS L., KALYTOVSKA M. 2003. Adsorption of cadmium on acid-modified Transcarpathian clinoptilolite. Microporous and Mesoporous Materials. Vol. 60(1–3) p. 183–196. DOI: 10.1016/s1387-1811(03)00376-7.
WARCHOŁ J., PETRUS R. 2015. Modeling of heavy metal removal dynamics in clinoptilolite packed beds. Microporous and Mesoporous Materials. Vol. 93. Iss. 1–3 p. 29–39. DOI 10.1016/j.micromeso.2006.01.021.
WOŁOWIEC M., BAJDA T. 2017. Current stage of knowledge relating to the use ferruginous sludge from water treatment plants – a preliminary review of the literature. Mineralogia. Vol. 48. Iss. 1–4 p. 39–45. DOI 10.1515/mipo-2017-0010.
YILDIZ S., SEVINС S. 2018. Heavy metal adsorption by dewatered iron-containing waste sludge. Ecological Chemistry and Engineering. Vol. 25. Iss. 3 p. 431–455. DOI 10.1515/eces-2018-0030.

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Authors and Affiliations

Christina Soloviy
1
ORCID: ORCID
Myroslav Malovanyy
1
ORCID: ORCID
Olga Palamarchuk
2
ORCID: ORCID
Iryna Trach
3
ORCID: ORCID
Halyna Petruk
4
ORCID: ORCID
Halyna Sakalova
4
ORCID: ORCID
Tamara Vasylinych
4
ORCID: ORCID
Nataliya Vronska
1
ORCID: ORCID

  1. Lviv Polytechnic National University, Viacheslav Chornovil Institute of Sustainable Development, Department of Ecology and Sustainable Environmental Management, Lviv, Ukraine
  2. Vinnytsia Mykhajlo Kotsiubynskyi State Pedagogical University, Educational and Scientific Institute of Pedagogy, Psychology, Department of Psychology and Social Work, Vinnitsa, Ukraine
  3. Vinnytsia National Technical University, Institute for Environmental Safety and Environmental Monitoring, Department of Ecology and Environmental Safety, Vinnitsa, Ukraine
  4. Vinnytsia Mykhajlo Kotsiubynskyi State Pedagogical University, Faculty of Natural and Geography, Department of Chemistry, Vinnitsa, Ukraine
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Abstract

In the last few years, cationic layered clays, including bentonites have been investigated as potential catalysts for SCR DeNOx systems. In this work, bentonite as the representative of layered clays was modified in order to obtain an alternative, low-cost NH3–SCR catalyst. Samples of raw clay were activated with HCl or HNO3, treated with C2H2O4 and subsequently pillared with alumina by the ion- exchange. Afterwards, the modified materials were impregnated with iron and copper. The obtained catalysts were characterized by XRD and FT-IR. SCR catalytic tests carried out over analyzed samples indicated the conversion of NO of approximately 90% for the most active sample. The type of acid used for modification and the type of active phase strongly influenced the catalytic properties of the analyzed materials.

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Authors and Affiliations

Agmieszka Szymaszek
Maciej Kubeł
Bogdan Samojeden
Monika Motak
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Abstract

Today, foundries are facing increasing demands for greener and more economical production while maintaining or improving the quality of the castings produced. The importance and use of green sand mixtures using bentonite as a binder are thus coming to the fore once again. They have the advantage of both eliminating the chemicalization of production and also allowing the immediate use of the already used mixture, including the binder, after adjustment of the composition and mulling. In order to maintain the quality of the resulting castings, it is necessary to monitor the properties of the moulding mixture through a series of laboratory tests. It is also essential to look at the processing quality of these mixtures, i.e. the combination of good mulling quality and efficient mulling time, which is often neglected. It is the quality of mulling and the effective mulling time that help to develop the bonding properties of the bentonite, improve the properties of the mixture, determine the efficiency of the muller and possibly reduce the time and energy required for mulling. The aim of this work is to present the effect of mulling on the properties of sand-water-bentonite mixtures. The properties studied are mainly the compactability, strength characteristics, moisture content of the mixture and the order of addition of raw materials.
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Bibliography

[1] Jelínek, P. & Mikšovský, F. (1985). Contribution to the evaluation of the efficiency of uniform green moulding mixture. Slévárenství. XXXIII (7), 268-274. (in Czech)
[2] Troy, E.C. et al. (1971). A Mulling Index Applied to Sand-water-bentonite. AFS Transactions. 79, 213-224.
[3] Strobl, S.M. (1995). How to improve green sands through more effective mulling. Modern casting. 85(2), 40-43.
[4] Thambiah, T.R. & Sarkar, A.D. (1973). Effect of mulling time on the properties of greensands. Foundry Trade Journal. 1973, 683-684.
[5] Headington, F., Rothwell, M.D. & Green, R. (1998). Available clay control and mulling efficiency. AFS Transactions. 1998, 271-291.
[6] Dietert, H.W., Graham, A.L. & Schumacher, J.S. (1971). How Mulling Time Affects Sand Properties. Foundry. 1971, 42-47.
[7] Kyncl, M. (2008). Evaluation of mixers efficiency. Diploma thesis, VŠB-TU Ostrava, Fakulta metalurgie a materiálového inženýrství, Ostrava, Czech Republic. (in Czech)
[8] Jelínek, P. (2004). Binder systems of foundry moulding mixtures – chemistry of foundry binders. (1st ed.). Ostrava. ISBN: 80-239-2188-6. (in Czech)
[9] Weniger, C.E. & Volkmar, A.P. (1970) A new control tool: a graph for evaluating effectiveness of available bentonite within foundry system sand. AFS Transactions. 1970, 17-24.
[10] Kumari, A., Murari, A.K., Prasad, U. (2020). Prediction of Green Sand Moulding Properties Using Artificial Neural Network. In U. Prasad (Eds.), Advances in Science & Technology (pp. 39-52). India: Empyreal publishing house.

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Authors and Affiliations

M. Gawronová
1
ORCID: ORCID
Š. Kielar
1
P. Lichý
1
ORCID: ORCID

  1. VSB-Technical University of Ostrava, Faculty of Materials Science and Technology, Department of Metallurgical Technologies, Czech Republic
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Abstract

Cut-off walls built using self-hardening slurries are an important tool for modern engineering pursuing Sustainable Development Goals. Much like cement concrete, this material is affected by the challenges posed by the increasing human pressure on the environment, although it is used significantly less widely than concrete; for this reason, relatively little comprehensive literature data is available describing the interaction of self-hardening slurries with the environment. This article provides a review that complements the current state of knowledge on self-hardening slurries in this area, with a particular focus on the durability of the material and its pollutant immobilization capabilities. To provide context, the material’s operating conditions, properties and components are briefly characterized. The resistance of self-hardening slurries to environmental aggression is described extensively, as it is a key factor in ensuring the durability of the material. A sample analysis of the material’s carbon footprint in several representative composition variants is presented. The subject of pollutant immobilization by self-hardening slurries is outlined. Lines of further research are proposed to fill gaps in the available knowledge.
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Authors and Affiliations

Łukasz Szarek
1
ORCID: ORCID
Łukasz Krysiak
1
ORCID: ORCID
Zbigniew Kledyński
1
ORCID: ORCID
Agnieszka Machowska
1
ORCID: ORCID
Paweł Falaciński
1
ORCID: ORCID

  1. Faculty of Building Services, Hydro and Environmental Engineering, Warsaw University of Technology, Nowowiejska 20, 00-653 Warsaw, Poland
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Abstract

This paper is a form of a report on conservation repairs on the internal walls of the semibasement of the Castle in Kórnik. One key element of these works is the desalination of the cellar walls. The excessive amount of salt results from a number of measures undertaken towards the end of the 19th c. and in the early 20th c., in order to rescue the architectural gem against a disaster. Carried out in the early 1950s, the cebertization (petrification of soil) proved to be the most spectacular measure leading to the stabilization of the structure. Unfortunately, however, this operation generates a side effect in the form of a huge amount of harmful salts, which permeate from the soil into the castle walls, leading to their gradual destruction.
In view of the progressing degradation of the walls in the castle cellars, measures leading to the elimination of the increased level of dampness and the damaging salts in the walls were implemented as of 2012. After works stabilising the level of dampness were carried out, the process of desalination, i.e. removal of salt from the structure of the walls, was undertaken as the subsequent stage – and is currently in progress. Special compresses placed onto the surface of the salinated building are used for the purpose.
The scale of the facility and the complexity of desalination itself resulting from the size and heterogeneity of the semibasement walls enforced the necessity to determine the appropriate scope of the works and assign them individually to each wall in the particular parts of the cellars. In the course of a year, in three stages, the majority of the wall surface was successfully covered with the first compress. The desalination method adopted does not bring about instant results, and the possibility to assess its final effects requires time.
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Authors and Affiliations

Katarzyna Wypych
1
ORCID: ORCID

  1. Biblioteka Kórnicka

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