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Article

Alkali Activated Paste and Concrete Based on of Biomass Bottom Ash with Phosphogypsum

by
Danutė Vaičiukynienė
1,*,
Dalia Nizevičienė
2,
Aras Kantautas
3,
Vytautas Bocullo
1 and
Andrius Kielė
1
1
Faculty of Civil Engineering and Architecture, Kaunas University of Technology, LT-44249 Kaunas, Lithuania
2
Faculty of Electrical and Electronics Engineering, Kaunas University of Technology, Studentu St. 48, LT-51367 Kaunas, Lithuania
3
Faculty of Chemical Technology, Kaunas University of Technology, Radvilėnų Pl. 19, LT-50254 Kaunas, Lithuania
*
Author to whom correspondence should be addressed.
Appl. Sci. 2020, 10(15), 5190; https://doi.org/10.3390/app10155190
Submission received: 9 July 2020 / Revised: 23 July 2020 / Accepted: 24 July 2020 / Published: 28 July 2020
(This article belongs to the Special Issue High-Performance Eco-Efficient Concrete)
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Abstract

:
There is a growing interest in the development of new cementitious binders for building construction activities. In this study, biomass bottom ash (BBA) was used as aluminosilicate precursor and phosphogypsum (PG) was used as a calcium source. The mixtures of BBA and PG were activated with the sodium hydroxide solution or the mixture of sodium hydroxide solution and sodium silicate hydrate solution. Alkali activated binders were investigated using X-ray powder diffraction (XRD), X-ray fluorescence (XRF) and scanning electron microscopy (SEM) test methods. The compressive strength of hardened paste and fine-grained concrete was also evaluated. After 28 days, the highest compressive strength reached 30.0 MPa—when the BBA was substituted with 15% PG and activated with NaOH solution—which is 14 MPa more than control sample. In addition, BBA fine-grained concrete samples based on BBA with 15% PG substitute activated with NaOH/Na2SiO3 solution showed higher compressive strength compered to when NaOH activator was used −15.4 MPa and 12.9 MPa respectfully. The NaOH/Na2SiO3 activator solution resulted reduced open porosity, so potentially the fine-grained concrete resistance to freeze and thaw increased.

Graphical Abstract

1. Introduction

In recent years, the amount of biomass bottom ash (BBA) originating from Lithuanian combustion plants is constantly increasing. This type of ash is classified as nonhazardous wastes, so BBA is deposited in local landfills. Consequently, it is very important to reuse ash and to reduce discarding at landfill site. According to Carrasco-Hurtado et al. [1] environmental study showed that the amount of heavy metals in BBA is usually lower than that in fly ash so for that reason it is possible to recycle it in construction materials.
Giergiczny et al. [2] investigated composite cement and concrete containing low-calcium and high-calcium fly ash and granulated blast furnace slag. When large quantities of ash or/and slag were incorporated in the cement system, the properties (e.g., long setting time, low early strength, etc.) of samples were improved. One utilization method for BBA could be the incorporation into construction materials. The chemical and mineral composition of BBA is appropriate for reusing in the production of new, low-carbon building materials. In this way, the replacement of traditional initial material [3,4] such as fly ash or slag in alkali activated materials (AAM) by BBA leads to important environmental benefits [5,6,7]. As demand for ecological alternatives to Portland cement like alkali activated materials (AAM) is growing, there is interest to utilize phosphogypsum (PG) in AAM. AAM binders are aluminosilicate materials like fly ash, slag, red clay that can be activated with an activator solution—NaOH, Na2SiO3, KOH, etc. Concrete produced with these raw materials has shown potential results: the compressive strength of alkali activated fly ash paste reaching over 25 MPa [8,9].
PG can expand the base of the AAM raw materials. Approximately 4.5–5.5 tons of PG is generated per ton of phosphoric acid production using wet process [10]. It is estimated annually 100–280 million metric tons of PG are generated globally. The PG waste is usually stockpiled in landfills. Landfilling stocks results leaching, and hazardous constituents get into groundwater and underlying soils [11]. Pérez-López et al. investigated PG deposited over Tinto river saltmarshes for 40 years until 2010. Study have shown the high potential of contamination of the whole PG stack, including those stack zones that were restored and supposedly should have stop leaching of toxic solutions [12].
Previous studies [13,14,15,16,17] show interest in using PG or gypsum in AMMs. Multiple studies have investigated the optimum amount of gypsum compounds and it was determined that the optimal amount of CaSO4 in alkali activated systems is close to 10% wt [13,14]. Gypsum takes significant part in the activation processes–it completely dissolves and participates in solid product formation. In the alkali’s activation reactions PG is a supplier of SO42− and Ca2+ ions enhancing the formation of secondary reaction products. When PG is present, portlandite and ettringite initially forms after dissolution form in AAM system. The hardened AAM consists mainly of amorphous hydration products, intermixed with thenardite and minor amounts of secondary gypsum. The incorporation of PG results in shorter initial setting time, but longer final setting time. There is significant increase of compressive strength when activator is NaOH [13]. The compressive strength development can be attributed to lower porosity [13,14]. PG decreases of Ca/Si ratios in the C–A–S–H gels and it could be the reason of a higher polymerized network [13]. The AAM samples with PG inclusion exhibited an average of 1.2 times greater residual strength than samples without PG, after being treated at 400, 600, 800 and 1000 °C temperatures [15]. Boonserm et al. [16] had found that the additive of flue gas desulfurization gypsum significantly improved the geopolymerization of the mixtures of bottom ash and fly ash. The compressive strength of samples increased too in that samples were up to 10% of gypsum was used. This increase is explained with the formation of additional amount of CSH. Similar results gave Khater et al. [17]. A 10% PG additive improved samples mechanical properties and microstructure. Samples were formed from the fly ash, PG and cement kiln dust mixtures. Rashad et al. [14] investigated the alkali activated fly ash and PG. When 5% or 10% of semi hydrate PG was incorporated in the system, the mechanical properties, improvement was detected. Chang et al. [18] investigated the influence of phosphoric acid and gypsum on the sodium silicate-based alkali-activated slag pastes. It was determined that the addition of phosphoric acid acted as a retarder.
In previous already published papers, alkali activated systems based on fly ash or fly ash and bottom ash with phosphogypsum were investigated. In this work, only biomass bottom ash was used as an aluminosilicate source. Some amount of BBA was substituted with PG. Both (BBA and PG) are local availability byproducts. The aim of this work is to investigate alkali activated paste and fine-grained concrete with BBA and PG, and to describe the effect of PG on the properties of newly formed AAM systems. Two types of alkali activators were used: NaOH solutions and the mixtures made from NaOH solution and sodium silicate hydrate (WG).

2. Methodology

2.1. The Characterization of Raw Materials and the Mixing Composition of Alkali Activated Biomass Bottom Ash Pastes and Concretes

In this study, the precursor was made from biomass bottom ash (BBA) which was obtained from the combustion plant located in Lithuania. First, this BBA was dried at 100 °C temperature for 24 h and then it was milled in ball mill.
The PG used in this work had α hemihydrate type. It is the waste product of orthophosphoric acid production. PG is formed by the reaction of sulfuric acid from natural apatite according this Equation (1) [19]:
Ca5(PO4)3 F + 5H2SO4 + 2.5H2O = 3H3PO4 + 5CaSO4⋅0.5H2O + HF;
The powder of PG was taken from the conveyor belt of waste removal and dried at 100 ± 5 °C temperature.
According to SEM analysis the BBA particles have irregular shape with angular morphologies (Figure 1a). Microscopic analysis showed that semihydrate phosphogypsum crystals are of dense structure and irregularly shaped parallelepipeds (Figure 1b).
The particle size distribution for BBA is presented in Figure 2a. The particles size is in wide range from 0.9 μm to 460 μm. The PG particles are finer (Figure 2b) and they are in the range from 0.8 μm to 38 μm. The specific surfaces areas according to Blaine for PG is 201 m2/kg and for BBA is 396 m2/kg.
The mean diameter of PG particles is 74.7 μm and for the particles of BBA is 58.6 μm.
The XRD analysis showed that in BBA dominated quartz, anorthoclase, gehlenite and calcium hydroxide with small amounts of calcium carbonate calcium oxide and magnesium oxide (Figure 3a). BBA has semi-amorphous semi-crystalline structure with a broad peak close to silica [20].
In the mineral composition of PG, according to XRD analysis (Figure 3b), dominated bassanite (CaSO4·0.5H2O) and a small amount of brushite (CaPO3(OH)·2H2O). PG exhibit well definite crystalline structure [21].
This byproduct of biomass combustion in power plants (BBA) has the relatively high calcium, silicon and alkali contents (Table 1).
According to the chemical composition of the PG, CaO and SO3 are the major components of this material (Table 1). There is some amount of acidic impurities such as P2O5–0.81%; including water-soluble—0.10% and F—0.14%, which make PG difficult to reuse. Loss on ignition was 6.4%. The pH of the water suspension–4.7.
Two types of alkali activators were used (Table 2). The first type was sodium hydroxide solution made with commercial NaOH pellets (analytical grades). The second one was made from the mixture of NaOH solution and the sodium silicate hydrate (WG) solution (silicate modulus 3.0, concentration 36%).
Paste samples size was 20 × 20 × 20 mm; their composition is given in Table 2. The BBA was substituted for PG at various amounts: 5%, 10%, 15%, 20% and 25%. The ratio of water and solid materials (BBA + PG) in the mixtures was regulated and ranged from 0.23 to 0.30. First, dry components were thoroughly mixed. Then, the mixtures were filled with the solutions of alkali activator (Table 2). These solutions were prepared by dissolving NaOH in water. When the complex alkali activator was used WG solution was filled to sodium hydroxide solution.
The total hydration duration was 28 days. The first day samples hydrated in room temperature, the second day at 60 °C temperature—and for the remaining 26 days, in room temperature again. All this time samples were covered with polyethylene covering materials which protect the samples from dehydration.
The sand from Kvesai quarry (Lithuania) was used as fine aggregate to produce alkali activated concrete samples the 0/4 fraction sand. The particle density of sand was 2.65 Mg/m3. The amount of initial materials for concrete samples is shown in Table 3.
The compressive strength of hardened AAM paste was evaluated after 7 and after 28 days. To perform the test a hydraulic press ToniTechnik 2020 was used. The compressive strength of samples was determined in accordance with EN 196-1:2005. At least of three samples were tested of each type and the Sample Standard Deviation (SSD) was calculated according to Equation (2):
S S D = ∑ ​ ( x − x ¯ ) 2 ( n − 1 ) ;
where, x takes on each value in the set; x ¯ is the average (statistical mean) of the set of values; n is the number of values.

2.2. The Experimental Techniques

The mineral composition of initial materials and AAM hardened pastes was carried out by using X-ray powder diffraction analysis. Data were collected by DRON-6 X-ray diffractometer with Bragg–Brentano geometry using Ni-filtered Cu Kα radiation and graphite monochromator, operating with the voltage of 30 kV and emission current of 20 mA. The step-scan covered angular range of 2–70° in steps of 2 = 0.02°. The powder X-Ray diffraction patterns were identified with references available in PDF-2 data base [22].
The chemical composition of BBA and PG was evaluated by using XRF analysis. For this purpose, a Bruker X-ray S8 Tiger WD using a rhodium (Rh) tube, an anode voltage Ua up to 60 kV and an electric current I up to 130 mA were used. The compressed samples were measured in a helium atmosphere [23]. The hydration water (loss on ignition, %) in phosphogypsum was calculated after heating the material at the temperature 400 °C. The pH phosphogypsum was measured with the AD8000 professional multi-parameter pH-ORP-Conductivity-TDS-TEMP bench meter, with a measuring range of −2.00 to 16.00 pH, a resolution of 0.01 pH and an accuracy of ±0.01 pH. The pH measurements of water suspensions were conducted when the ratio of water (W) and solid material (S) W/S was 10.
Microstructure investigation of BBA, PG and hardened pates was performed using a high-resolution scanning electron microscope ZEISS EVO MA10 [24]. The resolution of the images (of secondary electrons in a high vacuum) of this microscope is at least 3 nm with 30 kV and at least 10 nm with 3 kV. In the performed analysis, the acceleration voltage was 5 kV.
A laser particle size analyzer (CILAS 1090 LD) was used for the evaluation of the particle size of the BBA and PG. The distribution of solid particles in the air stream was 12 wt%–15 wt%. Compressed air (2500 mbar) was used as a dispersing phase [25].
The compressive and flexural strength of hardened AAM paste and fine-grained concrete samples were determined by using hydraulic press Toni Technik 2020 according to the EN 196–1. The size of hardened AAM paste samples was 20 × 20 × 20 mm. Fine-grained concrete samples were 40 × 40 × 160 mm prisms. For each data point at least tree samples were tested. The compressive strength of hardened AAM paste was evaluated after 2 and 28 days of hydration. The mechanical properties of fine-grained concrete samples were tested after 7 and 28 days.
The total and open porosity of alkali activated fine-grained concrete samples was evaluated by water absorption according to Skripkiunas et al. [26].

3. Results and Discussion

The compressive strength of alkali-activated BBA samples is shown in Figure 4. There are two types of samples: one type of hardened AAM pastes was alkali activated by using NaOH solutions and the mixture of NaOH and sodium silicate hydrate solutions was used in the second type of samples. When SiO2/Na2O molar ratio was 2 the samples containing 20% PG substitute had the highest compressive strength. In this case compressive strength reached 24.3 MPa and precursors were alkali activated with NaOH solutions (Figure 4a). Similar values of compressive strength (23.0 MPa) were obtained for that samples which were activated with the mixtures of NaOH and sodium silicate hydrate solutions. In this case the optimal content of PG substituting was 15% (by mass of BBA). In all investigated cases (Figure 4a) the substitution of BBA to PG had gains in compressive strength. This substitution is recommended not to exceed 25%. Similar compressive strength (25.83 MPa) had geopolymer samples formed with circulating fluidized bed combustion coal bottom ash according to Topçu et al. [27].
Figure 4b shows the compressive strength of the alkali activated BAA paste with SiO2/Na2O molar ratio 3. The positive effect was detected in this case. In the PG 15-3 samples with the alkali activator of NaOH solutions the highest compressive strength reached 30.0 MPa after 28 days. By using the same molar ratio but as alkali activator the mixture of NaOH and sodium silicate hydrate solutions was the compressive strength was reached 23.0 MPa after 7 days of hardening. After longer duration (28 days) of hardening, the reduction was observed of more than 3 times of compressive strength (8.0 MPa). This reduction of compressive strength may be explained by the fast alkali reactions resulted in quick strength gain after 2 days. This gain should be due the increase of gel like matrix. After 28 days the structure samples showed cracks on the surface which could be caused by the drying shrinkage (Figure 4b) [28]. In all investigated cases the use of calcium promoter such as PG which substituted BBA had positive effect to compressive strength gain. After 28 days the compressive strength was higher than compressive strength of reference samples. Similar results related with positive effect of calcium promoters in bottom ash geopolymer fine-grained concrete report Hanjitsuwanet al [29].
The mineral composition of alkali activated biomass bottom ash is shown in Figure 5. The X-ray diffraction study is carried out only on the 8 pastes because they are the ones that have shown the highest compressive strength values. The reference compositions were investigated as well. In all X-ray diffraction patterns it is possible to detect quartz and calcium hydroxide which left unreacted from BBA. During alkali reactions calcium silicate hydrate, calcium aluminum oxide hydroxide hydrate, sodium aluminum silicate hydrate formed. When PG was incorporated in the system, additional mineral calcium aluminum hydroxide hydrate formed (PG 20-2, PGWG 15-2, PG 15-3 and PGWG 15-3). The crystal phases remained the same in all samples and it did not depend on the molar SiO2/Na2O ratios which were used in this work. By using lower SiO2/Na2O molar ratio (SiO2/Na2O = 2) the higher amount of alkali had an impact on the formation of Na2CO3(H2O) (without PG) and Na2SO4 (with PG). The formation of Na2CO3(H2O) had negative affect on the development of compressive strength [30]. When PG was inserted in the alkali activated BBA, PG reacted with NaOH and this reaction products Na2SO4 with Ca(OH)2 were (Figure 5a). During hydration process, Na2SO4 is an effective activator for alkali activated binders [31]. Sodium sulfate could motivate the formation of calcium aluminum silicate hydrate and calcium silicate hydrate. As seen in Figure 5a,b, the main peak of calcium silicate hydrate is more intensive in the samples where PG was incorporated.
In the samples with higher amount of SiO2 the molar SiO2/Na2O ratio was 3. The peaks of new formed hydrates appear more intensive (Figure 5b). This could be related with formation of higher amount of polymerization products in alkali activated system. The hydroxy–sodalite was detected in the sample PGWG 15-3 [32].
Figure 6 shows the morphology of alkali activated biomass bottom ash after 28 days of hardening. PG 15-3 and PGWG 15-3 samples exhibited different microstructures. In the microstructure PG 15-3 sample varied honeycomb-like C–S–H and honeycomb type amorphous gel structures (Figure 6a) [33].
It can be observed that in the PGWG 15-3 sample showed a higher degree of microcracking and unreacted the particle of BBA were detected as well (Figure 6b) [34]. This PGWG 15-3 sample had a more compact microstructure by comparing with the microstructure of PG 15-3 sample. This compact microstructure is closely related to the increased amount of hydration products which increased the amount of microcracks [35].
The compressive and flexural strength of alkali activated fine-grained concretes are shown in Table 4. As the aluminosilicate precursor the mixture of BBA with PG was used. The two types of alkali activator solutions were chosen: sodium hydroxide solution and the mixture of sodium hydroxide solution and sodium silicate hydrate. The proportions of PG and BBA were chosen according to the values of paste samples compressive strength (Figure 4). According to Ding et al. [36] the compressive strength values of the alkali-activated pastes, fine-grained concretes and concretes with the same pastes were unequal. Fine-grained concretes had significantly lower compressive strength compared with the paste samples.
Chindaprasirt et al. [37] investigated and compared fly ash and bottom ash fine-grained concretes. The values of compressive strength are different for alkali activated fly ash and for bottom ash. Fly ash fine-grained concrete reached 35 MPa while bottom ash fine-grained concrete had compressive strength in the range of 10–18 MPa. Such a difference is explained by the degree of polymerization. The polymerization of bottom ash is lower than the fly ash during alkali activation. All these samples were cured at 65 °C for 48 h. In this work, samples were cured at lower 60 °C temperature and duration was shorter-24 h. The fine-grained concretes samples had similar compressive strength 12.9 MPa and 15.4 MPa when activated with NaOH solution and the mixture of NaOH/Na2SiO3 solution, respectively (Table 4). The higher compressive strength could be related with the higher amount of active silicon (sodium silicate hydrate solution) [38]. The flexural strength was similar for both types of fine-grained concretes. A little bit higher value of flexural strength (2.4 MPa) were obtained for the sample with mixture of NaOH solution and Na2SiO3 solution (CPWG 15-3) compared with CPG 15-3 sample.
The porosity study is carried out on the two-alkali activated fine-grained concrete samples shown in Figure 7. It is considered to be because they are the ones that have shown the highest compressive strength values. The X-ray diffraction study is carried out only on the 8 pastes because they are the ones that have shown the highest compressive strength values. The reference compositions were investigated as well. It is possible to predict the durability (freeze–thaw resistance) of alkali activated fine-grained concrete according to these parameters of porosity. The total porosity (P) is almost the same for both types of fine-grained concretes. The open porosity (Pa) which determined by water absorption of alkali activated fine-grained concrete was less (10.9%) for CPG 15-3 samples compared with CPWG 15-3 samples 13.4%. Different situation is with close porosity (Pu). In this case CPG 15-3 samples had higher 16.8% close porosity compared with CPWG 15-3 samples which had 14.1%. Therefore, the alkali activator of NaOH and Na2SiO3 solutions had influence on the formation higher amount of close porosity and lower amount of open porosity while the total porosity remained the almost the same in activated fine-grained concrete samples. According to Nagrockienė et al. [39] concrete with higher closed porosity have better freeze–thaw resistance. Hence, the fine-grained concrete activated with the NaOH and Na2SiO3 solution should have higher freeze–thaw resistance compared with fine-grained concrete activated with just NaOH solution.

4. Conclusions

In this study, the compressive strength of hardened alkali activated past and fine-grained concretes was determined. To improve the reaction degree of BBA calcium promoter such as PG was used. The following observation were made:
  • The higher values of compressive strength were detected when SiO2/Na2O molar ratio was three compared with the samples where samples had SiO2/Na2O = 2. When SiO2/Na2O molar ratio was two, the samples containing 20% PG substitute had the highest compressive strength (24.3 MPa) after 28 days, while compressive strength of the samples with SiO2/Na2O molar ratio three peaked after 28 days at 30.0 MPa;
  • Overall, paste samples activated with NaOH/Na2SiO3 solution were weaker compared activated with NaOH. The compressive strength peaked at 23.0 MPa after seven days with 15% PG substitute, but after 28 days was reduced to 8.0 MPa. The reduction could be attributed to the cracking caused by the drying shrinkage. In addition, SEM images showed a higher degree of microcracking and unreacted the particle of BBA were detected when NaOH/Na2SiO3 solution was activator;
  • The amount of PG substitute was 15%–20% of BBA mass and it is recommended not to exceed 25%. The higher amount of PG significantly reduced the compressive strength;
  • In contrary to paste samples, fine-grained concrete samples have shown different tendencies. When BBA with 15% PG was activated with NaOH/Na2SiO3 solution compressive strength reached 15.4 MPa after 28 days, but when the same precursors were activated with NaOH compressive strength was reduced by 16% (12.9 MPa). The higher compressive strength could be related with the higher amount of active silicon;
  • Even though total porosity of fine-grained concrete activated by NaOH and NaOH/Na2SiO3 solution was nearly the same −27.5% and 27.7% respectfully, there is difference in open and closed porosity. When sodium silicate was present the open porosity was reduced from 16.8% to 14.1%. Hence, the fine-grained concrete activated with the NaOH and Na2SiO3 solution should have higher freeze–thaw resistance;
  • After 28 days of hydration the highest compressive strength reached 30.0 MPa the samples activated NaOH solution and by using 15% of BBA substitution to PG. The possibility of potential use of BBA (silicon and aluminum sources) and PG (calcium source) as binder precursor for production of AAMs was confirmed. This can suggest a solution for both alkaline binders industry to provide a new precursor and fertilizers industry to solve the storage problems of PG.

Author Contributions

We all authors: D.V., D.N., A.K. (Aras Kantautas), V.B. and A.K. (Andrius Kielė) declare that we contributed to this article in equal parts about 20% everybody: D.V. and V.B. prepared the introduction part. Characterization of initial materials and the part of experimental procedures was prepared by D.N. and A.K. (Andrius Kielė). The parts of “Results and discussion” and “Conclusion” were written and evaluated by all authors. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Acknowledgments

This research work was supported by the Lithuanian Science Council project “The utilization of industrial waste in alkali-activated concrete”, project code P-MIP-17-363.

Conflicts of Interest

The authors declare no conflicts of interest.

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Applsci 10 05190 g001 550
Figure 1. Microstructure of (a) biomass bottom ash and (b) phosphogypsum.
Figure 1. Microstructure of (a) biomass bottom ash and (b) phosphogypsum.
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Figure 2. Granulometric composition of biomass bottom ash (a) and phosphogypsum (b).
Figure 2. Granulometric composition of biomass bottom ash (a) and phosphogypsum (b).
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Figure 3. The mineral composition (XRD analysis) of (a) biomass bottom ash and (b) phosphogypsum. Notes: Q—quartz, SiO2 (77–1070); CH—calcium hydroxide, Ca(OH)2 (84–1271); CC—calcium carbonate, Ca(CO)3 (72–1652); A—anorthoclase, (Na,K)(Si3Al)O8 (75–1631); G—gehlenite, Ca2 Al(AlSiO7) (79–2421); CO—calcium oxide, CaO (4–777); MO—magnesium oxide, MgO (78–430); C—bassanite, CaSO4·0.5H2O (33–310); B—brushite, CaPO3(OH)·2H2O (11–293).
Figure 3. The mineral composition (XRD analysis) of (a) biomass bottom ash and (b) phosphogypsum. Notes: Q—quartz, SiO2 (77–1070); CH—calcium hydroxide, Ca(OH)2 (84–1271); CC—calcium carbonate, Ca(CO)3 (72–1652); A—anorthoclase, (Na,K)(Si3Al)O8 (75–1631); G—gehlenite, Ca2 Al(AlSiO7) (79–2421); CO—calcium oxide, CaO (4–777); MO—magnesium oxide, MgO (78–430); C—bassanite, CaSO4·0.5H2O (33–310); B—brushite, CaPO3(OH)·2H2O (11–293).
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Figure 4. Compressive strength of alkali-activated biomass bottom ash pastes when SiO2/Na2O molar ratio is (a) 2 and (b) 3 (Table 2).
Figure 4. Compressive strength of alkali-activated biomass bottom ash pastes when SiO2/Na2O molar ratio is (a) 2 and (b) 3 (Table 2).
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Figure 5. X-ray diffraction patterns of alkali activated biomass bottom ash when SiO2/Na2O molar ratio is (a) 2 and (b) 3. Notes: Q—quartz, SiO2 (83–2465); Ch—calcium hydroxide, Ca(OH)2 (84–1268); K—calcium silicate hydrate, Ca1.5SiO3.5x H2O (33–306); T—thenardite Na2SO4 (74–2036); Z—sodium aluminum silicate hydrate Na96Al96Si96O384216H2O (39–222); N—sodium carbonate hydrate Na2CO3(H2O) (70–845); Hs—hydroxy–sodalite Na6(AlSiO4)6 8H2O (72–2329); H—alcium aluminum hydroxide hydrate Ca2Al(OH)7·3H2O (33–255).
Figure 5. X-ray diffraction patterns of alkali activated biomass bottom ash when SiO2/Na2O molar ratio is (a) 2 and (b) 3. Notes: Q—quartz, SiO2 (83–2465); Ch—calcium hydroxide, Ca(OH)2 (84–1268); K—calcium silicate hydrate, Ca1.5SiO3.5x H2O (33–306); T—thenardite Na2SO4 (74–2036); Z—sodium aluminum silicate hydrate Na96Al96Si96O384216H2O (39–222); N—sodium carbonate hydrate Na2CO3(H2O) (70–845); Hs—hydroxy–sodalite Na6(AlSiO4)6 8H2O (72–2329); H—alcium aluminum hydroxide hydrate Ca2Al(OH)7·3H2O (33–255).
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Figure 6. Microstructure of alkali activated biomass bottom ash samples (a) PG 15-3 and (b) PGWG 15-3.
Figure 6. Microstructure of alkali activated biomass bottom ash samples (a) PG 15-3 and (b) PGWG 15-3.
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Figure 7. The porosity of alkali activated fine-grained concrete samples. P—total porosity; Pa—open porosity; Pu—closed porosity.
Figure 7. The porosity of alkali activated fine-grained concrete samples. P—total porosity; Pa—open porosity; Pu—closed porosity.
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Table
Table 1. Chemical composition of initial materials, wt%.
Table 1. Chemical composition of initial materials, wt%.
CaOSiO2Na2OAl2O3MnOMgOK2OFe2O3P2O5TiO2SO3FOther
BBA49.022.40.282.510.308.298.692.185.050.330.58–0.39
PG38.600.37–0.13–0.04–0.030.81–53.480.146.4
Table
Table 2. The mixing composition of alkali activated biomass bottom ash pastes.
Table 2. The mixing composition of alkali activated biomass bottom ash pastes.
SamplesBBA, gPG, gWG, gH2O, g NaOH, gSiO2/Al2O3SiO2/Na2O
PG 0-21000–2320.112.02
PG 5-2955–2819.912.02
PG 10-29010–2918.812.02
PG 15-28515–3017.812.02
PG 20-28020–3016.712.02
PG 25-27525–3015.712.02
PGWG 0-2100020.02324.514.82
PGWG 5-295515.82822.614.32
PGWG 10-2901014.02921.214.22
PGWG 15-2851515.73020.514.62
PGWG 20-2802016.53019.714.92
PGWG 25-2752519.53019.415.62
PG 0-31000–2313.012.03
PG 5-3955–2912.412.03
PG 10-39010–3011.712.03
PG 15-38515–3011.112.03
PG 20-38020–3010.412.03
PG 25-37525–309.812.03
PGWG 0-310006.42313.013.33
PGWG 5-39557.12712.413.53
PGWG 10-390106.02811.713.33
PGWG 15-385157.33011.113.73
PGWG 20-380207.63010.413.93
PGWG 25-375259.7309.818.43
Table
Table 3. Mixing composition of alkali activated biomass bottom ash concrete, g.
Table 3. Mixing composition of alkali activated biomass bottom ash concrete, g.
IngredientsThe Activation with NaOHThe Activation with NaOH + Na2OnSiO2-mH2O
CPG 0-3CPG 15-3CPG 20-3CPWG 0-3CPWG 15-3CPWG 20-3
BBA450383360450383360
PG067.590067.590
Sand 0/4135013501350135013501350
NaOH58.549.746.858.549.746.8
Water glass00028.832.934.2
Water210210210200200200
Table
Table 4. Compressive strength, flexural strength and density of alkali activated fine-grained concretes samples.
Table 4. Compressive strength, flexural strength and density of alkali activated fine-grained concretes samples.
SamplesCompressive Strength, MPaFlexural Strength, MPaCompressive Strength, MPaFlexural Strength, MPaDensity (After 28 Days), kg/m3
After 7 Days of HardeningAfter 28 Days of Hardening
CPG 0-34.51 ± 0.261.52 ± 0.0510.94 ± 0.482.30 ± 0.121965 ± 14
CPG 15-34.79 ± 0.232.22 ± 0.0612.90 ± 0.452.31 ± 0.151971 ± 14
CPG 20-33.94 ± 0.221.39 ± 0.069.33 ± 0.412.00 ± 0.171853 ± 15
CPWG 0-36.42 ± 0.281.32 ± 0.0510.73 ± 0.421.84 ± 0.161998 ± 15
CPWG 15-38.40 ± 0.242.18 ± 0.0815.42 ± 0.432.41 ± 0.112019 ± 14
CPWG 20-36.20 ± 0.271.20 ± 0.0711.94 ± 0.311.54 ± 0.131885 ± 13

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MDPI and ACS Style

Vaičiukynienė, D.; Nizevičienė, D.; Kantautas, A.; Bocullo, V.; Kielė, A. Alkali Activated Paste and Concrete Based on of Biomass Bottom Ash with Phosphogypsum. Appl. Sci. 2020, 10, 5190. https://doi.org/10.3390/app10155190

AMA Style

Vaičiukynienė D, Nizevičienė D, Kantautas A, Bocullo V, Kielė A. Alkali Activated Paste and Concrete Based on of Biomass Bottom Ash with Phosphogypsum. Applied Sciences. 2020; 10(15):5190. https://doi.org/10.3390/app10155190

Chicago/Turabian Style

Vaičiukynienė, Danutė, Dalia Nizevičienė, Aras Kantautas, Vytautas Bocullo, and Andrius Kielė. 2020. "Alkali Activated Paste and Concrete Based on of Biomass Bottom Ash with Phosphogypsum" Applied Sciences 10, no. 15: 5190. https://doi.org/10.3390/app10155190

APA Style

Vaičiukynienė, D., Nizevičienė, D., Kantautas, A., Bocullo, V., & Kielė, A. (2020). Alkali Activated Paste and Concrete Based on of Biomass Bottom Ash with Phosphogypsum. Applied Sciences, 10(15), 5190. https://doi.org/10.3390/app10155190

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