Influence of Starkeya novella onMechanical andMicrostructural Properties of Cement Mortars

Cement-based materials are subject to degradation during their service life. Most of the structural failures have been associated with corrosion of the rebar due to chloride ingress, alkali aggregate reaction, and/or sulfate attack. Microbial activities, especially in waste water collection points such as sewer lines, may compromise the integrity of concrete structures. (is study reports an experimental work carried out to determine the effect of Starkeya novella bacteria species on mechanical and microstructural properties of cement mortars. Mortar prisms were prepared from selected ordinary Portland cement (OPC) and Portland pozzolana cement (PPC) in Kenyan markets. Bacterial solution of 1.0×10 cell/mL concentration was used as either mix water, curing media, or both. Distilled water was used to prepare mortar prisms for control samples. Compressive strength was determined after the 7, 28, 56, and 90 day of curing. Scanning electron microscopy (SEM) was tested on both bacterial and control mortar prisms after the 28 day of curing. Both PPC and OPC exhibited significant decrease in compressive strength for bacterial-prepared mortars as compared to controls. SEM analysis showed extreme erosion on the microstructure of the microbial mortars. (is was denoted by massive formation of ettringite and gypsum which are injurious to mortar/concrete.


Introduction
Concrete and/or mortar is used globally in large volumes for construction of roads, bridges, sewage systems, and/or railway lines [1]. Concrete and/or mortar durability is a key aspect in evaluating the service life of cement-based structures. Cement-based materials are subject to degradation due to influence of external processes such as carbonation, sulphate attack, and/or chloride ingress [1][2][3]. Exposure of concrete structures into aggressive environment initiates degradation mechanisms that result in failure and/or increased repair expenses of critical civil structures.
Most of transport and collection systems such as sewer lines are made of cement mortar/concrete. ese structures are susceptible to degradation due to microbial activities that enable a chemically aggressive environment suitable for degeneration of such structures [4]. Even though microorganisms form invisible thin biofilms on the surfaces of concrete, they are capable of degrading concrete-made structures [5,6]. While a number of studies have been conducted to investigate the effect of chemical sulphuric acid on the degradation of concrete, little attention has been given to degrading microorganisms present in aggressive environments such as sewer systems [7,8].
Microbial metabolism results in synthesis of hydrogen sulphide (H 2 S) by sulphur reducing bacteria (SRB) in the sewer lines. e formed hydrogen sulphide is biologically oxidized to form biogenic sulphuric acid (H 2 SO 4 ) [9]. e formed biogenic sulphuric acid lowers the concrete pH which is a suitable condition for biodegradation [10]. Additionally, the formed acid may react with cement mortar/ concrete constituents to form other deleterious expansive products such as gypsum and ettringite [10,11]. is form of concrete degradation is commonly referred to as microbially induced deterioration (MID) [4].
Structural failures due to MID reduces the service life of concrete-based structures from the projected 100 years to virtually 30-50 years. In severe environs, the service life of the concrete may be reduced to 10 years [12]. is form of concrete structural failures not only contributes to increased cost of repair, but it has a huge negative effect on health and environment. is is due to production of unpleasant gases such as hydrogen sulphide [4,[13][14][15]. Biodeterioration of cement-based materials involves a series of chemical, physical, and biological reactions that take place in an intricate system involving microbes, material, and the surrounding environment [16].
Concrete deterioration as a result of microbial attack was first documented by Parker [6]. He (Parker) isolated 5 strains of iobacillus species bacteria from corroded concrete surface and reported that the isolated bacteria strains had the ability to produce biogenic acid leading to concrete corrosion. Munyao et al., 2020 [17], reported that iobacillus intermedius degrades the microstructure of ordinary Portland cement mortar. Several other researchers have shown that the activity of iobacillus species in degrading concrete structures increases with increase in moisture, oxygen, and hydrogen sulphide [18,19].
In developing countries such as Kenya, there are many reported cases of structural failures that culminated to deaths and/or lose of properties. Majority of these failures are attributed to poor workmanship, inconsistency in quality of other materials such as sand, aggregates, and mixing water. While a lot of research in this region has been conducted to investigate the use of other cementitious materials such as pozzolans in improving the properties of existing ordinary Portland cement (OPC) and the desired quality of mixing water, very little attention has been given to the contribution of microbes on the performance of cement-based materials.
Starkeya novella formerly referred to as iobacillus novellus was first isolated by Starkey [20,21]. Some researchers were able to show that iobacillus novellus currently referred to as Starkeya novella has the ability to grow chemolithoautotrophically with thiosulphate as a source of energy [22]. e work conducted in this experiment involved simulated laboratory studies to determine the influence of Starkeya novella bacteria species on mechanical and microstructural properties of cement mortars of PPC and OPC.  [23] were sampled from a local cement manufacturing plant in Kenya. ISO standard sand purchased from the Societe Nouvelle Du Littoral company was used in preparation of test mortar prisms as described in EN 196-1 [24]. e composition of the test cements used in this experiment was as presented in  SO 4 ). Starkeya novella bacteria designated as DSM 506 was acquired from Leibniz-Institut DSMZ Deutsche Sammlung Von Mikroorganismen und Zellkulture GmbH, Germany. e culturing medium was prepared using sterilized distilled water.

Determination of Cement Oxides.
e chemical composition of each test cement was determined using X-ray fluorescence technique (XRF).
e PANalytical XRF equipment model Epsilon3 XLE was used in this experiment. 0.900 g of each test cement was accurately weighed in a platinum crucible and mixed with 9.000 g of lithium tetraborate as a flux. e resultant mixture was fused in a M4 gas fusion unit for a period of 17 minutes to form a glass bead. e formed glass beads were kept in a desiccator to cool before transferred into the XRF unit for analysis. Each test cement was analysed in triplicates, and the average values are tabulated as shown in Table 1.

Determination of Loss on Ignition (LOI).
Triplicate samples of each test cement were subjected to the loss on ignition test. LOI was determined gravimetrically as described in KS EAS 18:1-2017 [23]. 1.000 g of each test cement was accurately weighed and transferred in a silica crucible that had already been weighed and tared. e crucible with the sample was then placed in a furnace set at 975°C for a period of 1 hour. e crucible with the sample was cooled in a desiccator. LOI was expressed as a percentage of the difference of the mass before and after ignition.

Microbial Culturing of Starkeya novella. Culturing of
Starkeya novella was conducted at microbiology laboratories of the University of Embu, Kenya. e medium for the bacteria growth was formulated as described in the DSMZ manual. Definite amount of each of the reagents was accurately weighed and dissolved in 1000 mL of distilled water as shown in Table 2. e pH of the resultant solution was adjusted to 6.6 using a mixture of Na 2 CO 3 and NaHCO 3 . is was done to meet the desired optimal growth of the bacterium.
e achieved solution was sterilized by autoclaving at a temperature of 125°C. e sterilized solution was then cooled to a room temperature, and pure spores of Starkeya novella were carefully added. 10.0 g of Na 2 SO 3 .5H 2 O and 12.0 g of agar were added to serve as the source of nutrients to the bacteria. Incubation was carried out in a shaker kept at a temperature of 30°C for a period of 5 days. Bacterial concentration was maintained at 1.0 × 10 7 cell/mL. e obtained bacterial solution was preserved in a sterilized container for use in mixing and curing of mortar samples.

Preparation of Mortar Prisms.
Test cements were prepared and casted in moulds of size 40 mm × 40 mm × 160 mm as defined in KS EAS 148:1-2000 [25]. e test mortar prisms were prepared from both OPC and PPC. In each test cement, three sets of tests were conducted. e first set was the control sample which was cast and cured in distilled water. is particular set was labelled as OPC H 2 O (H 2 O) and PPC H 2 O (H 2 O). e second set involved preparation of test cement with bacterial solution as mix water and cured in distilled water. is particular set up was labelled as OPC SK (H 2 O) and PPC SK (H 2 O). e third set up involved casting of test cements with bacteria solution as mix water and curing of the mortar prisms in the bacterial solution. is particular set up was labelled as OPC SK (SK) and PPC SK (SK). In all scenarios, a standard water-tocement ratio (w/c) of 0.5 was used. e prepared mortar prims were kept in a humidity cabinet after casting for a period of 24 hours with the temperature and relative humidity maintained at 20°C ± 2°C and above 95%, respectively. Demoulding was done after 24 hours, and the mortar prisms cured in respective curing media maintained at room temperature.

Determination of Compressive Strength.
e compressive strength for both OPC and PPC mortars prepared and cured in different regimes as described in 2.2.2 was determined in accordance with KS EAS 148:1-2000 [25]. e mortar prism to be tested for strength was placed at the center of the platens of the compressive machine within ±0.5 mm and longitudinally such that the end face of the test prism overhang the platens or the auxiliary plates by about 10 mm. Increase of the load was done smoothly at the rate of 2400 ± 200 N/s over the entire load application until fracture. e strength development was determined after the 7 th , 28 th , 56 th , and 90 th day of curing using the compressive strength model YAW-300. e results obtained were expressed in Mpa.  is could have been attributed to slow growth of the microbes and hence too early to detect the deleterious effect. A similar trend was noted in OPC microbial mortars, OPC SK (H 2 O) and OPC SK (SK), at 7 days. However, the strength decrease was observed in microbial mortars for both test cements after 28 th days of curing. Figures 3 and 4 show compressive strength decrease of microbial mortars for PPC and OPC.

Results and Discussion
As shown in Figures 3 and 4, the compressive strength of PPC and OPC microbial mortars decreased with increase in the curing period. While there was a reported decrease in strength for the mortars prepared with bacterial solution and cured in water, denoted as PPC SK (H 2 O) and OPC SK (H 2 O), the extreme effect was observed on test prisms prepared and cured in bacterial solution, denoted as PPC SK (SK) and OPC SK (SK). is could perhaps be attributed to the deleterious effect of the Starkeya novella bacteria. Adverse effect was observed at the 90 th day of curing with OPC SK (SK) reporting a decrease of 34.25% against 17.94% in PPC SK (SK). e decline in compressive strength was attributed to biogenic sulphuric acid formed as a result of Starkeya novella activity. According to Starkey, 1935 [21], iobacillus novellus currently referred to as Starkeya novella species has the ability to oxidize thiosulfates present in soil into biogenic sulphuric acid. Furthermore, George et al., [29] observed that exposure of bacterial concrete to air and H 2 S results in oxidation of sulphur compounds to form H 2 SO 4 which attacks and disintegrates the concrete.
OPC is more prone to acid attack than PPC due to high amount of calcium hydroxide (CH).
e formed H 2 SO 4 may react with calcium hydroxide (CH) in the pore solution to form additional gypsum (CSH 2 ). e formed CSH 2 reacts with the C 3 A phase in cement to form ettringite (AFt) which is an expansive product. is is as shown in equations (1) and (2). Presence of ettringite (AFt) in concrete results in cracking. e formed cracks form suitable pathways for ingress of other harmful materials to the concrete matrix: All the test samples were subjected to SEM analysis after 28 days of curing. In all the scenarios, there was a significant comparison of the SEM micrographs with other researchers' works already published [17,30,31]. e SEM image for the OPC control sample, OPC H 2 O (H 2 O), as shown in Figure 5 was characterized by homogenous distribution of calcium hydroxide (CH) plates and calcium silicate hydrate (C-S-H) phase as the key hydration products. e presence of the needle-shaped crystals referred to as ettringite (AFt) could have perhaps been as a result of sulphate content from gypsum that is added to the ordinary Portland cement (OPC) to control the setting time and improve on the cement workability.

Scanning Electron
ere was no observable crack in the morphology of the control sample.
High presence of ettringite (AFt) and eroded CH plates was observed in OPC SK (H 2 O) as shown in Figure 6. Presence of high sulphate content provides a suitable environment for the development of ettringite. is was attributed to the metabolic activity of the Starkeya novella. According to Diercks et al., 1991 [32], and Sand and Bock, 1984 [33], presence of sulphur oxidizing bacteria (SOB) in     the sewer set up results in production of biogenic sulphuric acid. e formed biogenic sulphuric acid attacks CH and C-S-H as the key hydration products of OPC leading to formation of secondary expansive materials such as gypsum and ettringite [34,35].   Ettringite crystals were observed on the surface of the PPC control mortar as shown in Figure 8.
is was attributed to the gypsum added to control the setting time and improve on the workability of the cement. e ettringite was not as pronounced as compared to OPC control mortar shown in Figure 5. is was perhaps due to reduced C 3 A     Journal of Chemistry 7 content in PPC which provides a conducive environment for the development of ettringite. ere was significant decrease in CH plates for the control PPC as compared to control OPC.
is was attributed to pozzolanic activity. Silica and aluminate content from pozzolana reacts with CH to form additional CSH and CAH as shown in equations (3) and (4) [27,39]. e formed cementitious products make the resultant mortar denser and less permeable to attack by aggressive media. Similar observations were made by Muthengia, 2009 [28]. While there was appreciable increase in ettringite formation on bacterial treated mortars as shown in Figures 9 and 10, it was not as aggressive as observed in OPC bacterial treated mortars. is again was explained by the pozzolana reaction that hinders the attack of the resultant mortar from aggressive media [40]:

Conclusion
Based on the results of this work, Starkeya novella was found to reduce the compressive strength of both OPC and PPC mortars significantly.
is has a negative impact on the durability of structures exposed in such conditions. It was noted that OPC and PPC mortars prepared using distilled water and cured in bacteria solution denoted as OPC H 2 O (SK) and PPC H 2 O (SK) had a compressive strength decrease of 31.25% and 14.29%, respectively, whereas for OPC SK (SK) and PPC SK (SK), the strength decrease was 34.25% and 17.94%, respectively. It was further noted that Starkeya novella actively attacks OPC mortars more than PPC. is was evident from both the compressive strength and SEM results.

Data Availability
e data used to support the findings of work are available upon request through the corresponding author.

Conflicts of Interest
e authors declare no conflicts of interest.