Biocorrosion of concretes, mortars, and building materials and products is a serious problem wherever the conditions suitable for particular microorganisms occur. Biodeterioration reduces the utility efficiency of concretes, as well as their service life. Biocorrosion, as a specific type of chemical corrosion, is caused by various biogenic organic acids and mineral acids (sulphuric acid, H2
, and nitric acid, HNO3
), as well as by corrosive hydrogen sulphide, H2
S, and ammonia, NH3
, which result from the metabolic activity of microorganisms [1
]. These aggressive metabolites react mainly with calcareous components of concrete and mortar stone, with development of their non-binding calcareous salts. Some of them cause sulphate degradation, resulting in extreme expansion in the hardened concrete and leading to the complete destruction of concrete structural elements.
The effects of different concrete compositions and exogenously added nutrients on fungal colonization and fouling was studied in [5
]. Fungal strains belonging to the genera Alternaria
, and Trichoderma
were isolated directly from visibly fouled concrete structures and used individually and in a mix to inoculate mortar tiles varying in cement composition, supplementary cementitious material additions, water-to-cement ratio, and surface roughness. A strong positive relationship was observed between the tile water-to-cement ratio and the amount of biofouling. However, the addition of supplementary cementitious materials, such as fly ash, blast furnace slag, silica fume or metakaolin did not significantly affect biofouling in the mixed fungal community or T. viride
incubations. Blast furnace slag was added in varying amounts of 10%, 25%, and 50%, and the results indicated, that the slag had only a small antifungal effect [5
In contrast, it has been observed [6
] that ground granulated blast furnace slag (GBFS), as well as cements with GBFS content of ≥ 65 wt % possesses fungistatic properties. Therefore, fungistatic blast-furnace cements CEM III/A 32,5 N (with a GBFS content of 65 wt %), CEM III/B 32,5 N, and CEM III/C 32,5 N can be produced for achieving long-term fungistatic protection [6
]. Moreover, using GBFS as a concrete additive results in several advantageous concrete properties, such as a low hydration heat, high durability, low capillary porosity, high resistance to chloride penetration, sulphate, and thaumasite sulphate attack, and protection against alkali silica reaction [7
Generally, metallurgical slags are classified into two types: ferrous slag, which include iron slag generated in blast furnace processes and steel slags, and non-ferrous slag generated by the production of non-ferrous metals (Cu, Zn, Pb, Ni, etc.) [8
]. Ferrous metallurgical slags are determined by the kind of furnace from which they are generated. Different slag types originate from iron- and steelmaking processes [9
]. The main slag types produced from the iron- and steelmaking industries are classified as follows: (i) blast-furnace slags (ironmaking slags); (ii) steel-furnace slags (steelmaking and steel refining processes slags), further divided as follows: (a) basic-oxygen-furnace slag, (b) electric-arc-furnace slag, and (c) ladle furnace slag [9
]. Metallurgical slags are widely utilized for many construction and civil engineering purposes according to European standards, such as EN 197-1, EN 413-1, EN 14216, EN 206, EN 15167-1, EN 12620, EN 13043, EN 13055-1, -2, EN 13139, EN 13242, EN 13383-1, EN 13450, EN 14227-1, -2, -5, -10, -12, -13, etc. Steel-furnace slags are produced in smaller quantities than blast-furnace slags and are less widely used. It is estimated that one-half to two-thirds of steel-furnace slags produced worldwide are used either by recycling or in road building applications, road bases, fill, asphalt aggregate, railroad ballast, as fertilizers, soil conditioning, raw material for cement manufacture, etc. In some cases, specific aging or weathering requirements are stipulated to hydrate CaOfree
prior to use [10
]. Different types of slag have different capabilities for recycling and reuse; ladle furnace slag has the lowest such capability. About 80% of ladle furnace slag is currently landfilled, taking into account the whole of the EU [11
The article aims to study the antimicrobial efficiency of metallurgical slags for increasing their utilization in building materials and products, as well as for enlarging civil engineering applications with respect to higher biodeterioration resistance and sustainable development. Slag antimicrobial efficiency was determined by dilution methods in agar growth media, with the resulting concentrations of tested slags at 10, 20, 40, and 60%, and these were then mutually compared and also compared with a commercial biocide based on antimicrobial silver Ag.
2. Materials and Methods
The following types of metallurgical slags were tested: granulated blast-furnace slags with specific surface areas, such as 340 m2
/kg (S1a) and 520 m2
/kg (S1b); air cooled blast-furnace slag (S2); demetallized steel slag (S3); calcareous ladle slag (S4); and copper slag (S5). Most of them were ground to the specific surface area of 400 m2
/kg, except for S1a and S1b. The chemical composition of samples was analysed by X-ray fluorescence analysis (XRF) according to EN 196-2 using a SPECTRO X-LAB 2000 apparatus (Kleve, Germany). The semi-quantitative chemical composition of the slags is introduced in Table 1
The mineralogical composition of the samples was determined by the XRD technique using a BRUKER AXS D8 Advance device (Karlsruhe, Germany). The identified mineralogical composition of the slags is as follows: S1a and S1b—melilite (a solid solution of gehlenite C2AS and akermanite C2MS2); S2—melilite C2AS–C2MS2, brownmillerite C4AF, quartz SiO2; S3—wüstite FeO, brownmillerite C4AF, free lime CaO, portlandite Ca(OH)2, larnite β-C2S, quartz SiO2; S4—free lime CaO, larnite β-C2S, shanonite γ-C2S, gehlenite C2AS, C3A, gypsum CaSO4·2H2O, quartz SiO2 and S5—fayalite Fe2SiO4, anortite CAS2, pyroxene type CaAlAlSiO6. Biostat is a commercial biocide admixture based on antimicrobial silver Ag bonding to an Al2O3 support (Al2O3 99.62 wt %), with the efficient concentration of Ag at the level of 20 mg/g. Biostat is added in a proportion of 0.5 wt % in the thin layer applications, such as rendering and plastering mortars and of 1.0 wt % in rough, coarse layer applications, such as masonry mortar and bricklaying, to achieve an antimicrobial environment.
2.1. Determination of Free Calcium Oxide CaOfree Content in Ground Metallurgical Slags and pH of Water Leachates
The determination of free calcium oxide CaOfree
content in the metallurgical slags was performed using the hot ethylene glycol titration method. The slag sample was ground in the laboratory’s vibratory mill to a fineness with particle size under 0.1 mm sieve. Then 1.0 g of the slag sample was diluted with 75 mL of ethylene glycol in a filter flask. Afterwards, the solution was heated for half an hour with occasional stirring and then washed with 50 mL of denatured ethanol. Approximately 2–3 drops of alpha-naphthol phthalein was added to the solution as an indicator. The solution was then titrated with 0.1 N HCl, and the titration continued until the colour changed from blue to colourless. The CaOfree
content in the slag sample was calculated as follows: wt % CaOfree
= (the volume of 0.1 N HCl used for the titration; in millilitres) × 0.28. The CaOfree
content in the slags is given in Table 2
. The ground slags were leached in distilled water at 20 °C for 24 h. The pH was determined in the slag water leachates by an Agilent Technologies 3200 P pH Meter (Santa Clara, CA, USA) with an electrode reference system. The measured pH values of the water leachates are also shown in Table 2
No free lime CaOfree content was detected in slags S1a, S1b, and S5, very low CaOfree content in S2 and S3 and the highest CaOfree content was measured in S4 on the level of 3.30 wt %, respectively. The pH values of the ground slag water leachates were in the range of 9.34–12.93. The highest pH values > 12 were measured in leachates of slags S3 and S4, caused by the high free lime CaOfree content, and the lowest pH < 11 in leachates of slags S2 and S5. The water leached slags of S3 and S4 agglutinated into lumpy granules in water due to the hydration of free lime CaOfree, β-C2S, and in the case of S4 by the hydration of C3A with gypsum, as well. The hydrated lumpy granules were mechanically disaggregated to increase the leaching surface contact.
2.2. Determination of Antimicrobial Efficiency of Metallurgical Slags under In Vitro Conditions
The antimicrobial activity of the metallurgical slags was tested on selected representatives of biodeteriogenic microflora, such as bacteria, yeasts, and filamentous fungi. Microbial strains (bacteria and filamentous fungi) used in this work were either from the Czech Collection of Microorganisms, T.G.Masaryk University, Brno, Czech Republic (CCM) or yeasts from the Collection of Microorganism of the Institute of Biochemistry and Microbiology, Slovak University of Technology, Bratislava, Slovak Republic. Following microorganisms were used: G-positive bacteria—Bacillus subtilis CCM 178, Staphylococcus aureus CCM 3958, Micrococcus luteus CCM 410; G-negative bacteria—Escherichia coli CCM 3988, Pseudomonas aeruginosa CCM 3630, Serratia marcescens CCM 8587; yeasts—Candida utilis—1a, Rhodotorula glutinis—1; microscopic filamentous fungi—Aspergillus niger CCM-F 384, Penicillium funiculosum CCM 8080, Chaetomium globosum CCM 8156, Alternaria alternate CCM F-128, Trichoderma viride CCM F-534, Cladosporium herbarum CCM F-534. Gram-positive bacteria and Gram-negative bacteria differ in the thickness and chemical structure of their cell walls and, thus, also in sensitivity to antibiotics and other antibacterial agents.
2.2.1. Growth Media
The growth media used were as follows:
Meat-peptone bouillon (broth) for inoculation of bacteria (containing in 1000 mL of distilled water, 5 g meat extract, 5 g peptone for bacteriology and 2.5 g NaCl, with the pH adjusted from 7.2 to 7.4);
Meat-peptone agar for cultivation of bacteria (containing in 1000 mL of distilled water, 5 g meat extract, 5 g peptone for bacteriology, 2.5 g NaCl and 20 g agar, with the pH adjusted from 7.2 to 7.4);
Sabouraud’s glucose bouillon (broth) for inoculation of yeasts (containing in 1000 mL of distilled water, 20 g glucose and 10 g peptone for bacteriology, with the pH adjusted to 6.5);
Malt agar for cultivation of yeasts and filamentous fungi (containing in 1000 mL of distilled water, 60 g malt extract and 20 g agar, with the pH adjusted to 6.5).
For diluting the inoculum of bacteria and yeasts, saline solution (0.85% NaCl) was used, and for preparation of the spore suspension (filamentous fungi—moulds), a 0.1% water solution of Tween 80 was used.
2.2.3. Preparation of the Inoculum of Bacteria and Yeasts
A total of 25 mL of meat-peptone bouillon (broth) in a 100 mL Erlenmeyer flask was inoculated with a three-day-old culture of model bacteria using a bacterial loop, and 25 mL of Sabouraud’s glucose bouillon (broth) in a 100 mL Erlenmeyer flask was inoculated with a three-day-old culture of yeasts using an inoculation loop. The microorganism cultures were incubated for 15 h at 30 °C using shaking apparatus (at a vibration frequency 4 Hz). The grown microorganism cultures were aseptically filtered through three-ply gauze in order to remove possible clusters of cells. The obtained cell suspensions were diluted 100-fold with sterile saline (aqueous physiological solution) and were used for inoculation of the growth media (the cells concentration was 106 cells per mL) in order to determine the antibacterial and anti-yeast activity of the slag samples, respectively.
2.2.4. Preparation of Spore Suspension of Filamentous Fungi
A total of 8 mL 0.1% water solution of Tween 80 was aseptically added to the sporulated cultures of filamentous fungi, which had been cultivated on slant malt agar for 21 days. Spores from mycelium were loosened by bacterial loop, and filtered as above. The filtered spore suspension was diluted by sterile saline (the spores concentration was 2 × 107 spores per mL) and used for inoculation of the growth media in order to determine the antifungal activity of the slag samples.
2.2.5. Determination of Antimicrobial Activity
Meat-peptone bouillon for inoculation of bacteria, meat-peptone agar for cultivation of bacteria, Sabouraud’s glucose bouillon for inoculation of yeasts and malt agar for cultivation of yeasts and filamentous fungi were used as growth media. Saline solution was used for diluting the inoculum of bacteria and yeasts, and a water solution of Tween 80 was used for preparation of the spore suspension. Sterilization of growth media and solutions was realized in the laboratory autoclave at 120 °C for 20 min. The tests were performed in the laboratory incubator at temperatures of 30 °C for bacteria, 28 °C for yeasts and 25 °C for filamentous fungi at a relative humidity of 95%. Antimicrobial activity was determined by dilution methods in agar growth media, so that the resulting concentration of tested slags in growth media was 10, 20, 40, and 60%; further, the concentration of Biostat in growth media was 1.0 and 0.5%, respectively. The pH of the growth media with the addition of the slags was strongly alkaline (pH 11); thus, half the samples of each slag was tested at this pH, and the second half of the samples was tested at a modified pH (bacteria pH 7.2, yeasts, and filamentous fungi pH 6.6). The first half of the samples with the original pH represented real conditions for growth of microorganisms in concrete; the second half of the samples with a modified pH represented optimal conditions for growth of the microorganisms in vitro.
After sterilization, meat-peptone agar and malt agar with added slag samples and Biostat (at original pH and modified pH) were cooled down to 60 °C. The slag samples and Biostat were equally dispersed throughout growth media and subsequently they were divided and 6 mL of each was placed in the Petri dishes Ø 60.0 mm. Sterile paper discs (Ø 5.0 mm) were placed on the surface of solidified growth media, which were inoculated by 5 µL from spore suspension of model filamentous fungi on malt agar. The inoculation of bacteria and yeasts was done by direct pipetting the suspension on the surface of agarized media. Each 10 µL of suspensions were pipetted from the model bacteria onto meat-peptone agar or model yeasts on the malt agar.
The microorganisms were incubated in a thermostat at temperatures of 30 °C for bacteria, 28 °C for yeasts, 25 °C for filamentous fungi at a relative humidity of 95% for four days. The growth intensity of bacteria and yeasts was compared with the growth of bacteria and yeasts in the control growth media without slags. The growth of filamentous fungi in the presence of slags was monitored by the measurement of average diameter of growing colony at regular time intervals and was compared with the filamentous fungi growth in the control growth media without slags. In the case that no filamentous fungi growth with the presence of slags was observed, the paper discs with spores were transferred on fresh growth media. After 96 h incubation at 25 °C, the inhibiting effect of slags was inspected: fungistatic (spores germinate and subsequently the mycelium grows broader) and fungicidal—lethal (fungi do not grow; they are dead).
Firstly, the antimicrobial activity of individual slag samples on selected representatives of biodeteriogenic microflora was determined; subsequently the antimicrobial efficiency of individual slags was mutually compared. The test results on the antimicrobial efficiency of the individual slags are given in Table 3
, Table 4
and Table 5
. The antimicrobial efficiencies of slags regarding inhibition of growth of selected bacteria are given in Table 3
; the antimicrobial efficiencies of slags regarding inhibition of growth of selected yeasts are given in Table 4
; and the antimicrobial efficiencies of slags regarding inhibition of growth of selected filamentous fungi are given in Table 5
, respectively. The antimicrobial efficiencies of the metallurgical slags are compared with the antimicrobial efficiencies of the commercial biocide admixture Biostat. The growth extent of selected bacteria and yeasts is expressed by mathematical signs (-, +, ++, +++), and the degree of growth of selected filamentous fungi is expressed relatively by the percentage (%) of the sample surface covered by fungi colonies (measured against a K–control growth media without slags; with the expression of the c–fungicidal effect and s–fungistatic effect). The tests were also carried out at A–alkaline pH of growth media and N–neutral pH of growth media.
3.1. Antimicrobial Efficiency of Metallurgical Slags with Growth of Selected Bacteria
The results of determining the antibacterial efficiency of the individual slag samples and Biostat on the selected model Gram-positive bacteria (G+
) and Gram-negative bacteria (G−
) are given in Table 3
. Based on the obtained results, it can be stated that the inhibitory effect of the slag samples differs. Slag S4, which intensely inhibited growth of G+
and also G−
bacteria, had the highest antibacterial activity, which was also proven at the lowest concentration of slag S4: 10% in growth media. The bacteria, except M. luteus
, did not grow at higher concentrations of slag S4 in growth media, whereas the pH values of the growth media (alkaline, neutral) did not affect the inhibition intensity of bacterial growth.
The growth of G+ bacteria S. aureus and B. subtilis was inhibited in the presence of slag S3. The growth of G+ bacteria S. aureus and B. subtilis was inhibited by slag S3 in growth media as early as at a concentration of 10%, and at higher concentrations growth was completely inhibited. However, slag S3 did not affect the growth of G− bacteria, except for E. coli, at the highest concentration used (60%). Inhibition of bacterial growth in the presence of slag S2 was more intensive in the alkaline pH of growth media. The complete inhibition of the growth of G+ bacteria S. aureus and B. subtilis was detected with slag S2 at concentrations of 20, 40, and 60% in growth media and, inhibition of growth of G− bacteria E. coli, S. marcescens and P. aeruginosa was detected at a slag S2 concentration of 60% in growth media. Slag S2 only completely inhibited the growth of B. subtilis at a neutral pH of growth media; however, it did so at all tested concentrations. Slag S1a caused total inhibition of B. subtilis growth at concentrations of 40 and 60% in growth media at both a neutral and alkaline pH. The growth of S. aureus under conditions of 60% concentration of slag S1a in growth media at a neutral pH was completely inhibited.
A 40 and 60% concentration of slag S1b in growth media at neutral as well as alkaline pH led to total inhibition of the growth of B. subtilis. No growth of E. coli was observed at a slag S1b concentration of 60% in growth media at neutral pH. Slag S5 did not significantly affect the growth of the model bacteria. Slags S1a, S1b, S2 and S5 caused a change in S. marcescens growth at alkaline pH. The bacteria S. marcescens under these circumstances lost its red pigment and grew as a white colony.
Biostat at a concentration of 1.0% in growth media caused 100% inhibition of the growth of all model bacteria at neutral and alkaline pH. Only slight or no bacterial growth was observed at a Biostat concentration of 0.5% in growth media, while pH had no effect on their growth. Based on the obtained results, it can be stated that the antibacterial efficiency of the individual slag samples decreased in the order: S4 > S3 > S2 > S1a = S1b > S5. An overview of the testing arrangement in Petri dishes regarding the inhibition of bacteria growth in the presence of slag S4 and alkaline pH of growth media is shown in Figure 1
3.2. Antimicrobial Efficiency of Metallurgical Slags regarding Growth of Selected Yeasts
The results of determining the anti-yeast efficiency of the individual slag samples and Biostat on the selected model yeasts are given in Table 4
. Slag S4 possessed the highest anti-yeast activity. Growth of all model yeasts was completely inhibited at concentration as low as 10% of slag S4, at both alkaline and neutral pH of the growth media. Slags S1a, S1b, and S3 caused total inhibition of the growth of all model yeasts from a concentration of 20% in growth media at alkaline and neutral pH, as well. The growth of the model yeasts was intensively reduced in the presence of slag S2 at concentrations of 40 and 60% in growth media. Slag S5 partially inhibited the growth of the model yeasts; however, total inhibition of the growth of yeasts was not observed even at the highest concentration of 60% in growth media.
Biostat at a concentration of 1.0% in growth media caused complete inhibition of growth of all model yeasts at alkaline, as well as neutral, pH. However, the intensive growth of yeasts was observed at Biostat concentration of 0.5% in growth media, and so Biostat did not demonstrate an inhibiting effect on the growth of yeasts at 0.5% concentration. Based on the measured results, the anti-yeast efficiency of the individual slag samples decreased in the order: S4 > S1a = S1b = S3 > S2 > S5. An overview of the testing arrangement in Petri dishes regarding the inhibition of yeasts growth in the presence of slag S1a in neutral pH (N) and alkaline pH (A) of growth media is shown in Figure 1
3.3. Antimicrobial Efficiency of Metallurgical Slags regarding the Growth of Selected Filamentous Fungi
The antifungal efficiency values of the individual slag samples and Biostat on the selected model filamentous fungi are given in Table 5
. Growth of Alternaria alternata
was most intensively inhibited by slag S4. Total inhibition of A. alternata
growth was observed at concentrations of 40 and 60% of slag S4 in growth media at neutral as well as alkaline pH, particularly at a concentration of 20% in growth media at alkaline pH. Slag S4 even had a fungicidal (lethal) effect on the fungal spores of A. alternata
at a concentration of 60% in growth media at neutral pH, while slag S1b hindered the growth of A. alternata
at a concentration of 60% in growth media at neutral as well as alkaline pH. Slags S1a and S3 completely inhibited A. alternata
growth at a concentration of 60% in growth media, but only at neutral pH of the growth media. Slag S2 at concentrations of 40 and 60%, and slag S5 at a concentration of 60% in growth media, partially inhibited the growth of model A. alternata
. Based on a comparison of growth intensity of A. alternata
in the presence of the tested slags, the sequence of decreasing inhibition efficiency of the individual slags was in the order: S4 > S1b > S1a = S3 > S2 > S5.
Growth of Penicillium funiculosum was significantly inhibited by all tested slags; besides analogically, as with the previous model microorganisms, the highest growth inhibition was detected in the presence of slag S4. Based on a comparison of the growth intensity of P. funiculosum in the presence of the tested slags, the sequence of inhibiting efficiency of individual slags decreased in the order: S4 > S3 > S1a > S1b > S5 > S2. Total growth inhibition of Aspergillus niger was detected in the presence of all tested slags, with the exception of slag S5, at a concentration of 10% in growth media at both neutral and alkaline pH. Slag S4 possessed a fungicidal (lethal) effect on the fungal spores of A. niger at a concentration of 60% in growth media at neutral pH. The sequence of inhibiting efficiency of individual slags on A. niger growth decreased in the order: S4 > S1a = S1b = S2 = S3 > S5. No Trichoderma viride growth was detected in the presence of all tested slags, with exception of slag S5, at a concentration of 10% in growth media at alkaline pH. Slag S4 had a fungicidal (lethal) effect on fungal spores of T. viride at a concentration of 60% in growth media at alkaline as well as neutral pH. The inhibiting efficiency of the individual slags on T. viride growth decreased in the order: S4 > S1a = S1b = S2 = S3 > S5.
Slag S4 possessed the highest inhibiting efficiency on Cladosporium herbarum growth. Complete growth inhibition of the fungal biodeteriogen C. herbarum was detected at all tested S4 concentrations, with the exception of a concentration of 10% in growth media at alkaline pH, when the growth inhibition of C. herbarum was on the level of 40%. No growth was detected in the presence of S1b and S3 slags at a concentration of 60% in growth media at either neutral or alkaline pH and in the presence of S1a at neutral pH in growth media. Partial growth inhibition of C. herbarum was observed in the tested slags S2 and S5. The comparison study of the growth intensity of C. herbarum in the presence of the tested slags showed that the inhibiting efficiency of the individual slags decreased in the order: S4 > S3 > S1b > S1a > S5 > S2. Total growth inhibition of Chaetomium globosum was detected in the presence of slag S4, even from the lowest concentration of 10% in growth media. Similarly, complete growth inhibition was observed in the presence of slags S1a and S5, however, only at high concentration values of 40 and 60% in growth media, and as in the presence of slag S3 even at the highest concentration of 60% in growth media. Partial growth inhibition of Ch. globosum was observed in the presence of slags S1b and S2. A comparison of growth intensity of Ch. globosum in the presence of the tested slags showed a decreasing inhibition efficiency of individual slags in this order: S4 > S1a = S5 > S3 > S1b > S2.
From the above-mentioned results, it is evident that the model filamentous fungi used were sensitive to the presence of slag samples in various ways. As is apparent from the results of inhibition, all slags inhibited the growth of filamentous fungi by 40–100% at a concentration of 60% slag. The most sensitive to the presence of all slags were A. niger and T. viride. Their growth was completely inhibited when 20–60% concentrations of all slag samples at neutral and alkaline pH were used. The growth of these two fungi species was stopped, thus causing a fungistatic effect. A 60% concentration of slag S4 led to the inhibition of T. viride growth with fungicide effect (killed fungal spores). Slag S4 had the most inhibiting activity for all fungi. It completely inhibited growth of almost all model filamentous fungi in concentrations from 20–60% at alkaline pH, with mostly a fungistatic effect. Only T. viride growth was inhibited totally with a fungicide effect at alkaline pH of growth media at a slag S4 concentration of 60%. At neutral pH of growth media, the growth of model filamentous fungi was inhibited completely at concentrations from 40–60% of slag S4 and at slag S4 concentration of 60% with fungicide effect on A. alternata, A. niger, T. viride and Ch. globosum.
A lower inhibiting effect on filamentous fungi growth was observed in the case of slags S1a, S1b and S3, but they inhibited the growth of all tested filamentous fungi from 40–100% at a concentration of 40%. The lowest impact on the growth of model filamentous fungi was observed in the presence of slags S2 and S5 in growth media, which affected only the growth of the most sensitive fungi, A. niger
and T. viride
. The most resistant was A. alternata
. Its growth was most intensely inhibited by slag S4, with total inhibition observed at 40–60% of slag, with mostly a fungistatic effect. Biostat, at a concentration of 0.5% in growth media, did not affect the growth of model filamentous fungi, with exception Ch. globosum
, the growth of which was inhibited by 40%. Biostat at a concentration of 1.0% in growth media inhibited the growth of filamentous fungi by 30% to 70%. Based on the test results, it can be stated that Biostat is characterized mainly by antibacterial and anti-yeast efficiency, and affects the growth of model filamentous fungi only to a minimum extent. Regarding the fact that model filamentous fungi were selectively sensitive to the presence of the tested slags, it is possible to determine only an approximate order of inhibition efficiency of the slags to filamentous micromycetes: S4 > S3 = S1a = S1b > S5 > S2. The pH values of the growth media did not significantly influence the intensity of inhibition of the model microorganisms’ growth. A view of the testing arrangement in Petri dishes regarding the inhibition of Penicillium funiculosum
growth in the presence of slag S1a in alkaline pH (A) of growth media is shown in Figure 1
The results gained by testing the antimicrobial efficiency of individual slag samples on selected representatives of biodeteriogenic microflora can be summarized as follows: the tested slag samples are characterized by selective toxicity on the model bacteria, yeasts, and microscopic filamentous fungi; calcareous ladle slag (S4) possesses the highest antimicrobial efficiency; slag S4 best inhibits the growth of bacteria, yeasts, and microscopic filamentous fungi of all tested slags; total growth inhibition of Trichoderma viride and Aspergillus niger was detected in the presence of all tested slags at a concentration of 10% in growth media, except for copper slag (S5); the calcareous ladle slag (S4) and granulated blast-furnace slag with a specific surface area of 340 m2/kg (S1a) possessed fungicidal (lethal) effect on spores of some filamentous fungi at a concentration of 60% in growth media; copper slag (S5) is characterized by the lowest antibacterial and anti-yeast efficiency, despite having the highest Cu, Cr, Co, Ni, As, Zn, Pb, and Hg contents from all tested slags; air cooled blast-furnace slag (S2) and copper slag (S5) have the lowest antifungal efficiency. Biostat at concentrations of 0.5% and 1% in growth media inhibited the growth of bacteria, at a concentration of 1% inhibited the growth of yeasts, at a concentration of 0.5% did not affect the growth of filamentous fungi at all, and at a concentration of 1% inhibited the growth of filamentous fungi only to a minimum extent. However, the mechanism and biochemical processes of the antimicrobial efficiency of the metallurgical slags should be the subject of further study.
Generally, calcareous ladle slag (S4) possesses the highest antimicrobial efficiency and inhibits the growth of bacteria, yeasts and microscopic filamentous fungi most of all the tested slags. Slag S4 is characterized as having the highest CaO content of 58.97 wt % and the highest CaOfree
content (3.30 wt %) as well as the highest pH (12.93), in comparison with the other tested slags. Antimicrobial activity of metallurgical slags, with their very high CaO and CaOfree
contents, as well as their very high pH of water leachate, as in the case of slag S4, could be roughly similar to the antimicrobial efficiency of lime [12
]. However, calcareous metallurgical slags cause an increase in the pH values of water leachates up to the range of about 11.5–12.9 due to their high CaO content, e.g., similarly in the case of granulated blast furnace slag, cements and cement and granulated blast furnace slag mixtures, and concretes in the wet state, when they hydrate [1
], which affects the viability of microorganisms. This effect is similar to the effect of lime during sanitisation (hygienisation). Disinfection by lime at a wastewater treatment plant reduces the number of microorganisms extensively when operated at pH 11.2 [12
]. Lime enables the destruction of all pathogens due to the pH effect; it provides alkaline hydrolysis, combined with the temperature increase that quicklime hydration brings (thermolysis) [13
]. Of course, the thermolysis effect can be excluded in the case of metallurgical slags in comparison with lime, but alkaline hydrolysis can be considered as an antimicrobial potential of metallurgical slags. Alkaline hydrolysis (OH−
) results in the destruction of protein-based cellular walls and of enzymes, the destruction of proteins at polypeptide bonds to amino acids and oligopeptides, the destruction of nucleic acids (RNA), the destruction of carbohydrate cell constituents and lipids and the denaturing of enzymes [13
]. In order to grow, microorganisms need certain optimal environmental conditions (humidity, nutrients, osmotic pressure, temperature, light, pH of surroundings, etc.), which guarantee their optimal growth. Microorganisms grow at pH values from 2.5 to 9, and the optimal value of pH for growth of various microorganisms lies in the interval from 5 to 7.5, although exceptions do exist. In general, most microorganisms grow in a neutral or slightly alkaline environment (pH = 7 and slightly over pH > 7), whereas the majority of filamentous fungi (moulds) requires an acidic environment, i.e., a pH lower than 7. As long as the antimicrobial substances in a wet environment increase the pH value over pH > 7, the growth of fungi decreases and at the pH > 9 also the growth of bacteria. It is possible to achieve biocide (deadly) effect on microorganisms by a pH increase [1