Investigation of the Use of Recycled Concrete Aggregates Originating from a Single Ready-Mix Concrete Plant

Featured Application

Recycling of the major by-products from a ready-mix concrete plant within the plant as concrete aggregates.

Abstract

The waste produced from ready-mixed concrete (RMC) industries poses an environmental challenge regarding recycling. Three different waste products form RMC plants were investigated for use as recycled aggregates in construction applications. Crushed hardened concrete from test specimens of at least 40 MPa compressive strength (HR) and crushed hardened concrete from returned concrete (CR) were tested for their suitability as concrete aggregates and then used as fine and coarse aggregate in new concrete mixtures. In addition, cement sludge fines (CSF) originating from the washing of concrete trucks were tested for their properties as filler for construction applications. Then, CSF was used at 10% and 20% replacement rates as a cement replacement for mortar production and as an additive for soil stabilization. The results show that, although there is some reduction in the properties of the resulting concrete, both HR and CR can be considered good-quality recycled aggregates, especially when the coarse fraction is used. Furthermore, HR performs considerably better than CR both as coarse and as fine aggregate. CSF seems to be a fine material with good properties as a filler, provided that it is properly crushed and sieved through a 75 μm sieve.

1. Introduction

The construction industry has put considerable effort over the past years into becoming more sustainable [1]. The sustainability efforts of the industry involve practices such as energy conservation, waste minimization, and recycling. These practices apply to all aspects of construction activity, including cement and concrete production, and one important sector of concrete production is ready-mixed concrete. It is estimated that ready-mixed concrete production accounts for 350 million tons per year in the EU in 2016 [2], and the waste associated with this production varies greatly depending on local construction practices and is estimated at about 0.5–2% of the total production [3]. The waste streams generated from the ready-mix concrete plants (RMC) also vary, depending on the waste management strategies employed. The literature indicates several waste management strategies for RMC plants: some strategies include the use of the washing-out process for reclaiming the aggregates from the fresh concrete returns [4], the direct use of the fresh concrete returns in downgraded concrete products [5], and water reclamation by pressuring the sedimentation tanks [6]. The main solid wastes generated from RMC are hardened concrete from trial mixes or concrete testing, returned fresh concrete, and sludge fines from the washing of trucks. All of these materials could be used, potentially, in new construction products as recycled aggregates [7,8,9].

The use of recycled aggregates in concrete is of paramount importance for the sustainability of the construction industry, either seen from the point of view of natural resource scarcity [10] or from the point of view of waste and landfilling minimization [11]. As in most recycling processes, it is not an easy task; recycled aggregates originate from various sources and their quality level is not guaranteed [12]. Typically, they have inferior properties compared to natural aggregates [13,14] and, furthermore, they pose some technical difficulties (contaminants, higher absorption, etc.) [15,16]. However, a great number of researchers have explored the possibilities of using recycled aggregates in concrete in a beneficial way, either by suggesting ways of upgrading the product [17,18,19,20] or by categorizing and directing the proper quality of recycling aggregates to a suitable application [21,22,23].

The present report focuses on three main waste products from RMC, in the form of recycled aggregates from hardened good quality concrete (HR), recycled aggregates from hardened fresh concrete returns (CR), and recycled cement sludge fines from the washing of the concrete trucks (CSF). HR was produced by crushing test concrete specimens, typically used in the quality control of RMC concrete batches. In order to have a good-quality recycled aggregate, concrete specimens with an original compressive strength of 40 MPa or higher were selected for crushing, as it is shown from the literature that the original strength of the concrete influences the properties of the recycled aggregate and of the new concrete [24,25]. CR was also produced from crushing hardened concrete; however, prior to unloading the trucks, it is common that a considerable amount of water is used to ease the placing process. Therefore, CR originated from a lower-strength concrete than HR and was expected to be of lower quality. Kou et al. (2012) suggest that CR aggregates should be used in concrete mixtures with a w/c ratio as low as 0.35. HR and CR were tested for their suitability as concrete aggregates before substituting natural aggregates in test concrete mixtures. CSF has been found to consist mostly of hardened and unhydrated cement grain and fine aggregate [26]. It is a fine material which can be easily ground and sieved to a small size and has the potential to be used as a construction material [27].

In the present report, HR and CR were considered as recycled concrete aggregates (both coarse and fine) and were tested in concrete mixtures. On the other hand, CSF was considered as a filler and was tested separately. Following an investigation on the use of similar fine materials [28,29,30], and after investigating its physicochemical properties, CSF was tested in the present research as a material for soil stabilization at a 10% and 20% addition rate and as a filler, substituting 10 and 20 wt %. of cement in mortars.

The recycled aggregates from RMC have the benefit of being recycled concrete aggregates (RCA) without any mixed construction and demolition waste inclusions, which renders them acceptable for many standards regarding the use of RCA in concrete [31]. In addition, if they can be recycled on-site in new concrete products, then two other benefits compared to other RCAs arise; they are expected to have less fluctuation in properties compared to RCA from various sources, and there are no transportation costs. The pretreatment required for such aggregates (drying, crushing, sieving and soaking) can easily be carried out within the RMC plant [32,33]. Therefore, the recycling of considerable amounts of RMC waste would render the plant more sustainable and environmentally friendly.

2. Materials and Methods

2.1. Recycled Concrete Aggregates (HR and CR)

Crushed limestone (L) was used as a reference aggregate, as it is the most common aggregate used in concrete production in Greece. Fresh concrete returns (CR) and recycled concrete of high compressive strength (HR) were crushed and sieved in order to achieve the same gradation as limestone aggregates.

The recycled aggregates (HR and CR) were used as natural coarse aggregate replacements or as both fine and coarse aggregate replacements in concrete mixtures. The different fractions of recycled aggregates were examined separately since they typically have different properties, such as different water absorption and different amounts of adhered mortar [34,35,36]. The replacement ratio of either the fine or coarse fraction was selected to be 100%, in order to determine clearly the effect of aggregate substitution on the properties of the new concrete, although the optimum replacement ratio is usually less than 100% [37,38]. The aggregates under investigation were tested for their physical and chemical suitability for use in concrete, as well as for their durability.

2.1.1. Recycled Aggregate Properties Testing

The aggregate tests that were conducted were the sand equivalent test according to EN 933-8 and methylene blue test according to EN 933-9, in order to determine the quantity and quality of their fines. Grain size distribution was measured according to EN 933-2, in order to simulate similar aggregate gradation to that of the natural aggregates. Density (bulk, dry, saturated surface dry) and water absorption for the saturated-surface dry (SSD) condition were determined in order to perform the concrete mix design. Since water absorption for the recycled aggregates is usually higher than that of natural aggregates, the recycled aggregates were used in the SSD condition in order to have the same effective w/c ration in all mixtures. X-ray diffraction analysis (XRD) was used for the determination of the mineralogical composition, with a PW 1840 Phillips diffractometer (Philips, Amsterdam, Netherlands) and Ionic Chromatography for the determination of the water-soluble sulfate salts content (SO₃ wt %), with Dionex CS-1100, Thermoscientific Instruments (ThermoFisher Scientific, Waltham, USA). Regarding the assessment of the durability of the recycled aggregates, two tests were carried out: resistance to fragmentation (Los Angeles test) according to EN 1097-2 and resistance to freezing and thawing according to EN 1367-1.

2.1.2. Design of Concrete Mixtures

Five concrete mixtures were prepared in the laboratory and their terminology is given in

Table 1. Terminology for all concrete mixtures.

Mixture	Designation
LL	Reference (100% of aggregates limestone)
CR55	Recycled fresh concrete returns as coarse aggregates
CR100	100% of aggregates recycled fresh concrete returns
HR55	Recycled concrete of high compressive strength as coarse aggregates
HR100	100% of aggregates recycled concrete of high compressive strength

. The reference concrete mixture with limestone aggregates (LL) was a standard C25/30 mixture with maximum aggregate size of 16 mm. All concrete mixtures were produced using 300 kg/m³ cement CEM II32.5, 0.55 effective water/cement ratio and 1.5 kg/m³ superplasticizer. Limestone coarse aggregates (4–16 mm fractions) were replaced in mixtures CR55 and HR55 by CR and HR aggregates, respectively. The total amount of aggregates in mixtures CR100 and HR100 consisted of CR and HR, respectively. All the aggregates were added in a saturated-surface-dry condition by estimating the water absorbed by the aggregates and pre-soaking them. Each fraction of each gradation (i.e., 0.25–0.50 mm, 0.50–1.00 mm, etc.) was separately sieved for the three aggregate types used, so that the aggregate gradation curve would be the same for all mixtures. These particle-size distribution curves are shown in Figure 1. The final proportions of all mixtures are presented in

Table 2. Proportions of all mixtures in kg/m³.

Concrete Composition	LL	CR55	CR100	HR55	HR100
Cement CEM II32.5	300	300	300	300	300
Tap water	165	165	165	165	165
Fine aggregate 0–4 mm	842	843	528	843	499
Coarse aggregate 4–8 mm	478	478	300	478	283
Coarse aggregate 8–16 mm	576	525	525	542	542
Superplasticizer	1.5	1.5	1.5	1.5	1.5

. All specimens cast were cured at 20 °C and 95% RH until testing.

2.1.3. Fresh and Hardened Concrete Testing

In order to assess the fresh properties of the test mixtures, the air content, bulk density and consistency by the slump test of fresh concrete were measured according to EN 12350. Hardened concrete was tested for its mechanical properties and durability with the following tests:

• Open porosity according to RILEM CPC11.3 in water under vacuum;
• Seven and 28-day compressive strength test in 150 mm cubes (at least three for each testing age and mix);
• Elastic modulus in 150 × 300 mm cylinders (at least three for each testing age and mix);
• Three-point bending strength in 100 × 100 × 400 mm prisms (at least three for each testing age and mix);
• Drying shrinkage by 100 × 100 × 1000 mm, cured in 20 °C and <50% RH;
• Resistance to chloride ion penetration according to ASTM C 1202-97;
• Freeze–thaw resistance with de-icing salts after 10 cycles according to CEN/TS 12390-9.

2.2. Cement Sludge Fines (CSF)

Cement sludge fines (CSF) were obtained from the same RMC plant as the recycled aggregates, in wet condition. Figure 2 and Figure 3 show the sedimentation tanks and the storage of CSF in the RMC plant, while Figure 4 shows the CSF as received. The measured moisture in CSF was 42% and, therefore, it was left to dry in laboratory conditions for 2–3 days and then oven-dried at 100 °C until a constant mass was reached. After drying, it was crushed and sieved in order to obtain a fine material passing from the 75 μm sieve. The chemical composition of CSF and of the reference CEM I42.5 cement used were determined using atomic absorption spectroscopy, AAnalyst 400, Perkin Elmer. Additionally, their water-soluble salts were determined using ionic chromatography, Dionex, while simultaneous DTA-TGA (differential thermal–thermogravimetric analysis), SDT 2960 TA Instruments, was used for the determination of the calcium carbonate (CaCO₃) content of CSF, under an N₂ atmosphere from 10 °C to 1000 °C. The particle size distribution of CSF was determined with a Malvern Mastersizer 2000 analyzer. Furthermore, strength activity tests with lime according to ASTM C593-95 were performed, in order to determine its potential pozzolanicity.

2.2.1. CSF as a Replacement of Cement in Mortars

CSF was considered as a filler material and it was used as 10 and 20 wt %. Portland cement CEM I 42.5 replacement in mortars. All mixtures were prepared using a cement/siliceous river sand ratio of 0.33 and a water/binder ratio of 0.50. The fresh mortars were tested for bulk density and consistency and were cured at 20 °C and 95% RH until testing. Compressive strength was measured in 40 × 40 × 40 mm cubes (at least three for each testing age and mix) at ages of 3, 7 and 28 days. Additionally, X-ray diffraction analysis (XRD) was used for the determination of the mineralogical composition of the mortar with 20% CSF, and the porosity of hardened mortars was measured according to RILEM CPC11.3 in water under vacuum, after the completion of 28 days.

2.2.2. CSF as an Additive for Soil Stabilization

A well-known use of filler materials is for the improvement of poor soils, and CSF was also tested as an additive for soil stabilization. A sample of a low-quality reference soil with a 5% California Bearing Ratio (CBR) value was taken from a metro station excavation site in Thessaloniki, Greece. Two addition rates of CSF in soil were examined: 10 and 20 wt %. The maximum dry density and optimum moisture content according to the modified Proctor test and the CBR coefficient of soils were measured and compared.

3. Results and Discussion

3.1. Recycled Concrete Aggregates (HR and CR)

3.1.1. Recycled Aggregate Test Results

With the sand equivalent test, the calculation of SE value gives an estimation of the percentage of fines (aggregate particles that pass the 0.063 mm sieve). For higher SE values, the percentage of fines decreases. The results of the test are given in Figure 5. The higher concentration of fines was observed for CR, which can be explained by the high w/c ratio of concrete returns, which reduces the mechanical properties of the cement paste attached on the aggregates and thus produces more fines during crushing. On the other hand, in HR aggregates, the fines concentration is relatively low since the hardened cement paste is of high strength.

After identifying the content of fines in the recycled aggregates, it was considered necessary to determine if any clay particles exist in these fines and also measure the particle size distribution of aggregates. The results of the methylene blue test that was conducted for this purpose can be seen in Figure 6. It was observed that, for CR aggregates, a higher amount of injected dye solution is required, which is an indication of clay concentration. On the contrary, the concentration of clay in HR fines is insignificant. Since CR is 100% recycled concrete, the existence of clay can be attributed to storing and handling these aggregates in the facility of RMC.

Table 3. Aggregate test results.

	CR Fine	CR Coarse	HR Fine	HR Coarse
WA24 (%)	6.13	5.45	5.88	3.21
pa (kg/m³)	1723	2604	1617	2610
prd (kg/m³)	1558	2281	1477	2409
pssd (kg/m³)	1654	2405	1563	2486
LA	-	31.1%	-	36.5%

shows the results of water absorption (WA₂₄), particle bulk density (p_a), particle dry density (p_rd), particle saturated-surface-dry density (p_ssd) and Los Angeles coefficient (LA) tests. CR seems to absorb more water compared to HR, which is an indication of lower quality. However, the densities of the two aggregates do not differ essentially. The LA coefficient of CR was lower, but comparable to HR, and both aggregates have acceptable resistance to fragmentation according to the EN 12620 categorization. The mineralogical compositions of the raw materials CR and HR are given in Figure 7 and Figure 8. The presence of calcite and quartz in both materials is related to the binder attached on the aggregates, as well as tri-calcium–silicate compounds (C₃S) traces. The C₃S in CR was attributed to unhydrated forms of cement. Additionally, portlandite content (P) originating from the hydration of cement paste was found in HR.

The durability test results for CR and HR regarding mass loss (wt %) after 10 cycles of freezing–thawing are given in Figure 9. HR aggregates showed better results compared to CR. The mass loss of both aggregates is less than the upper category limit of 40% according to EN 12620.

The sieved representative samples (<0.75 mm) of CR and HR were collected in order to quantify their water-soluble sulfate salts, utilizing ionic chromatography. Sulfate salts were found in a low proportion in the mate and HR, respectively.

Although both CR and HR originate from hardened concrete, with a recycled concrete content of 90% or higher, it seems clear that HR is a higher quality aggregate, as expressed by the water absorption values, the fines quality characterization and the durability testing.

3.1.2. Concrete Test Results

The results of the fresh concrete tests are shown in

Table 4. Fresh concrete properties.

	LL	CR55	CR100	HR55	HR100
Air content (%)	2	2	2.3	2.2	2
Slump (cm)	6.5	11	17	15	18
Density (kg/m³)	2418	2318	2165	2378	2157

. Slump values increased as the rate of recycled aggregate increased, which can be attributed to the method of achieving the SSD condition of the aggregates, with HR aggregates showing better results. The recycled aggregates have been soaked with the amount of water required to reach the SSD state; however, it is not certain if the aggregates have actually absorbed all the water in the presoaking process or if they produced free water during the mixing process, mainly due to their porous nature. It is very probable that they did not remain completely saturated and that an amount of free water was released from the aggregates, resulting in an increased w/c ratio and increased workability. Of course, there is a reduction in the strength of the concrete with recycled aggregates, which is attributable to this excess water. The air content of all mixtures was around 2%, regardless of the type of aggregates used. The density seemed to decrease as the rate of recycled aggregates in the mixture increased, but the reduction is greater, as expected, when the fine recycled aggregates are used.

The results of the tests that were conducted on hardened concrete are given in

Table 5. Hardened concrete tests.

		LL	CR55	CR100	HR55	HR100
Open porosity (%)		13	11	21	10	22
Compressive strength (MPa)	7-day	33	22	18	28	27
	28-day	38	28	20	34	33
28-day flexural strength (MPa)		7.03	5.36	4.87	6.10	5.05
28-day elastic Modulus (GPa)		44.7	40.2	25.3	40.8	27.6
28-day drying shrinkage (μstrain)		180	400	590	220	300
Resistance to chloride Ion penetration	Charge passed	2491	3912	8284	2913	9342
	Chloride ion penetrability	MODERATE	MODERATE	HIGH	MODERATE	HIGH
Freeze–thaw mass loss (wt %)		0.422	0.362	0.845	0.412	0.890

, while in Figure 10, various mechanical properties of the recycled-base mixtures (Xi) are compared to the corresponding ones of reference concrete (X_LL). HR-based mixtures showed increased mechanical properties compared to those with CR aggregates and were lower compared to reference concrete. The open porosity was similar to that of the reference concrete when coarse recycled aggregates were used, but it increased considerably when the fine recycled aggregate was used. Compared to LL, HR 55 and HR100 showed a reduction of compressive strength of only 11% and 15%, respectively, which indicates that even the finer fraction of HR does not reduce the compressive strength of the produced concrete considerably. The flexural strength and elastic modulus, on the other hand, rely more on the quality of the interfacial transition zone between the aggregate and the cement paste, and the reduction in these values is in the range of 9–13% and 28–38% for HR55 and HR100, respectively. This implies that the bond between the fine aggregates and the cement paste was weaker when fine HR was used. Regarding CR, however, CR 55 and CR100 showed a reduction of compressive strength by 26% and 47%, respectively, which corresponds with the lower properties of CR measured earlier and the same trend applied for flexural strength and elastic modulus.

Regarding the durability tests, as shown in Table 5, the concretes with coarse CR and HR showed similar chloride ion penetrability to the reference concrete, while the mixtures with both fine and coarse recycled aggregates showed considerably higher penetrability. This can be attributed to the increased porosity of CR100 and HR100, which allowed the chloride ions to enter the concrete mass. Freeze–thaw results serve only as an indication of durability, since more cycles are usually required; however, the tested concretes with only coarse recycled aggregates seem to perform in a similar way to the reference concrete. The drying shrinkage results, as shown in Figure 11, show that HR aggregates, regardless of size, perform better than CR aggregates. In particular, concrete HR55 was closer to the reference concrete, while CR100 showed a distinct increase in shrinkage and, hence, reduced durability, which corresponds to the previous tests.

In general, the mechanical properties of concrete decreased as the rate of recycled aggregates increased. However, the mixtures with coarse recycled aggregates (CR55 and HR55) showed only a minimal decrease in both mechanical and durability properties when compared to the reference concrete. Furthermore, there is a clear distinction between the two types of recycled aggregates, as HR performed better than CR in all cases. In the cases of compressive strength and drying shrinkage, concrete with both fine and coarse HR showed better results than concrete with only coarse CR. These results, along with the initial test results on the materials, imply that HR aggregates are of better quality than CR aggregates and should be managed separately within the RMC plant and directed at different applications.

3.2. Cement Sludge Fines (CSF)

The chemical composition of the CSF, OPC (CEM I42.5 N) and soil used are shown in

Table 6. Chemical composition of CSF and cement I42.5 N.

(wt %)	Na2O	K2O	CaO	MgO	Fe2O3	Al2O3	SiO2	L.I.%	Cl−	NO3−	SO3
CSF	0.19	0.21	32.09	1.05	1.26	2.45	36.51	25.22	0.01	<0.01	0.05
CEM I42.5 N	0.57	1.08	66.84	3.91	2.40	3.74	19.55	1.91	0.03	0.02	1.49
Soil	0.90	0.98	8.67	5.39	3.79	6.88	63.14	10.25	0.08	0.02	0.02

, while their particle size distribution in comparison to that of CEM I42.5 is shown in Figure 12. CSF consists mostly of hardened cement paste and fine limestone aggregates; therefore, its CaO and SiO₂ contents were not expected to be reactive. The high value of loss on ignition can be attributed to the bonded water proportion and CO₂ quantity that was emitted from the sample, while the DTA-TG results (Figure 13) indicated a small amount portlandite (0.18 wt %) and the presence of a high amount of CaCO₃ (67.77 wt %).

The XRD diagram (Figure 14) shows that the mineralogical composition of CSF was mainly calcite. Also, an absence of C₃S and traces of C₂S peaks were observed. The latter may indicate full hydration of sludge. Also, a strength development test with lime according to ASTM C593-95 showed minimal strength development at 28 days (<0.50 MPa), which implies that there is no significant pozzolanic activity from CSF. The results of the analytical tests imply that CSF is probably a fine material without any hydraulic or pozzolanic properties. The fact that it can be easily crushed and sieved through the 75 μm implies that CSF could be used as a filler material. Regarding handling and processing, it would be preferable to use CSF in its original wet condition in order to avoid the drying process; however, further research is required in this direction.

3.2.1. CSF as a Cement Replacement in Mortars

The results of compressive strength testing are displayed in Figure 15. Mortar with a 10% replacement of cement by CSF reached almost the same strength levels as the reference. The early strength was slightly lower than the reference; however, the 28-day strength was slightly higher compared to reference. The mortar with 20% CSF showed a 7% reduction of strength compared to the reference. These results can be attributed to the filler effect [39], while the XRD results (Figure 16) on 28-day mortar samples with 20% CSF confirm the absence of ettringite. When a filler is added in a certain percentage, it influences the pH value of the binders in the pore solution. If the pH is reduced, this affects the hydration and as a result the compressive strength [40].

The decrease of compressive strength when 20% CSF was added can be related to the calcite content of CSF and its behavior as filler. Similar results have been observed by Nehdi et al. when limestone filler was used for cement substitution in mortars [41]. The porosity of mortar with 10% CSF was 6.6% and of mortar with 20% CSF was 10.3%, showing an increase compared to the reference mortar with no CSF inclusion, which had 3.5% porosity. This increase can be attributed to the porous nature of the hydrated cement mortar present in CSF, in a similar manner to the porous nature of fine recycled aggregates.

3.2.2. CSF for Soil Stabilization

The soil used as a reference had the chemical composition shown in Table 6, while its Atterberg limits were as follows: liquid limit LL: 56, plastic limit PL: 29.4 and plasticity Index PI: 26.6. Overall, it was categorized as poor for subgrade. Figure 17 shows the dry density versus moisture content for soil with 0%, 10% and 20% soil addition. As shown in

Table 7. Soil stabilization test results.

	0% CSF	10% CSF	20% CSF
Maximum dry density (g/cm³)	1.73	1.78	1.81
Optimum moisture content (%)	14.0	12.4	10.6
CBR (%)	5	12	33

, the dry density increased as the CSF rate increased while the required moisture in order to reach the maximum dry density reduced. Both of these properties are desirable for soil stabilization, but the most significant increase is that of the load-bearing capacity of soils, expressed by the CBR value. Furthermore, a higher percentage of CSF increased the CBR value even more. A similar strength increase has been reported (at lower addition percentages) when using lime for soil improvement [42,43].

The considerable increase in the CBR value of the soil treated with CSF implies that it can serve as a potential soil stabilization material, provided that it is primarily tested for micropollutants. The higher addition rate required compared to other possible additions (lime, cement) is not a great disadvantage, as CSF is a low-value industrial by-product. Also, Figure 17 shows that that soil with 20% CSF addition was more sensitive to water variation compared to soil without CSF, which needs to be taken account at the design stage.

4. Conclusions

The main conclusions drawn from the research can be summarized as follows:

• The properties of the recycled aggregates produced within a single RMC plant vary greatly, despite the fact that they are recycled concrete aggregates, without any mixed construction materials. Therefore, they should be managed separately and directed to suitable applications;
• All three recycled aggregates tested can be potentially be used in construction applications, after simple processing (crushing, sieving and pre-soaking), indicating that they do not require the energy and cost for transportation outside the RMC plant;
• The recycled aggregates from hardened concrete specimens (HR) had better properties compared to recycled aggregates from concrete returns (CR) and the use of their fine fraction could also be considered for structural concrete production;
• The durability properties of concrete with HR and CR were slightly reduced when 100% of the coarse fraction was used and considerably reduced when 100% of the fine and coarse fraction was used. Future research could determine the optimum amount of natural aggregate replacement, as in all recycled aggregates;
• CSF seems to be a good-quality fine material, provided that it is crushed and sieved through the 75 μm sieve;
• CSF could potentially be used as a filler material in cement mortar production and as an additive for soil stabilization.