Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Feb 2;14(3):686.
doi: 10.3390/ma14030686.

Laboratory Test to Evaluate the Resistance of Cementitious Materials to Biodeterioration in Sewer Network Conditions

Affiliations

Laboratory Test to Evaluate the Resistance of Cementitious Materials to Biodeterioration in Sewer Network Conditions

Amr Aboulela et al. Materials (Basel). .

Abstract

The biodeterioration of cementitious materials in sewer networks has become a major economic, ecological, and public health issue. Establishing a suitable standardized test is essential if sustainable construction materials are to be developed and qualified for sewerage environments. Since purely chemical tests are proven to not be representative of the actual deterioration phenomena in real sewer conditions, a biological test-named the Biogenic Acid Concrete (BAC) test-was developed at the University of Toulouse to reproduce the biological reactions involved in the process of concrete biodeterioration in sewers. The test consists in trickling a solution containing a safe reduced sulfur source onto the surface of cementitious substrates previously covered with a high diversity microbial consortium. In these conditions, a sulfur-oxidizing metabolism naturally develops in the biofilm and leads to the production of biogenic sulfuric acid on the surface of the material. The representativeness of the test in terms of deterioration mechanisms has been validated in previous studies. A wide range of cementitious materials have been exposed to the biodeterioration test during half a decade. On the basis of this large database and the expertise gained, the purpose of this paper is (i) to propose a simple and robust performance criterion for the test (standardized leached calcium as a function of sulfate produced by the biofilm), and (ii) to demonstrate the repeatability, reproducibility, and discriminability of the test method. In only a 3-month period, the test was able to highlight the differences in the performances of common cement-based materials (CEM I, CEM III, and CEM V) and special calcium aluminate cement (CAC) binders with different nature of aggregates (natural silica and synthetic calcium aluminate). The proposed performance indicator (relative standardized leached calcium) allowed the materials to be classified according to their resistance to biogenic acid attack in sewer conditions. The repeatability of the test was confirmed using three different specimens of the same material within the same experiment and the reproducibility of the results was demonstrated by standardizing the results using a reference material from 5 different test campaigns. Furthermore, developing post-testing processing and calculation methods constituted a first step toward a standardized test protocol.

Keywords: biodegradation; cementitious materials; durability; microorganisms; mortar; sewer; sulfuric acid.

PubMed Disclaimer

Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
Scheme of the sawn mortar specimen with the side covered with an epoxy resin.
Figure 2
Figure 2
(A) Biogenic Acid Concrete (BAC) test pilot; (B) Schematic diagram of the BAC test [13].
Figure 3
Figure 3
Scheme of one exposed cementitious specimen with the location of the feeding tubes and the collection tube for the leaching solution sample.
Figure 4
Figure 4
Evolution of the pH of the leaching solution during the exposure period.
Figure 5
Figure 5
Evolution of the sulfate concentration in the leaching solution during the exposure period.
Figure 6
Figure 6
Evolution of the standardized leached calcium as a function of the leached sulfate during the exposure period.
Figure 7
Figure 7
Evolution of standardized leached calcium per square meter as a function of the cumulative leached sulfate for the same testing campaign on four different materials
Figure 8
Figure 8
Cumulative leached sulfate from different testing campaign using the BAC test.
Figure 9
Figure 9
Evolution of the standardized cumulative leached calcium per square meter in function of the cumulative leached sulfate in the leached solution.
Figure 10
Figure 10
Evolution of the standardized cumulative leached calcium per square meter relative to the ordinary Portland material in the same campaign as function of the cumulative leached sulfate in the leached solution.

References

    1. WHO/UNICEF . Progress on Household Drinking Water, Sanitation and Hygiene 2000–2017. Unicef/WHO; Geneva, Switzerland: 2019. 140p
    1. Kaempfer W., Berndt M. Estimation of service life of concrete pipes in sewer networks. Durab. Build. Mater. Compon. 1999;8:36–45.
    1. Parker C.D. Species of sulphur bacteria associated with the corrosion of concrete. Nature. 1947;159:439–440. doi: 10.1038/159439b0. - DOI - PubMed
    1. Parker A.C.D. Mechanics of Corrosion of Concrete Sewers by Hydrogen Sulfide. Sewage Ind. Waste. 1951;23:1477–1485.
    1. Boon A.G. Septicity in sewers: Causes, consequences and containment. Water Sci. Technol. 1995;31:237–253. doi: 10.2166/wst.1995.0240. - DOI