Interference of manganese removal by biologically-mediated reductive release of manganese from MnOx(s) coated filtration media

Abstract

Discontinuing application of pre-filter chlorine is a common water treatment plant practice to permit a bioactive filtration process for the removal of soluble Mn. However, soluble Mn desorption has sometimes been observed following cessation of chlorine addition, where filter effluent Mn concentration exceeds the influent Mn concentration. In this paper it is hypothesized that Mn-reducing bacteria present in a biofilm on the filter media may be a factor in this Mn-release phenomenon. The primary objective of this research was to assess the role of Mn-reducing microorganisms in the release of soluble Mn from MnO x(s) -coated filter media following interruption of pre-filtration chlorination. Bench-scale filter column studies were inoculated with Shewanella oneidensis MR-1 to investigate the impacts of a known Mn-reducing bacterium on release of soluble Mn from MnO x(s) coatings. In situ vial assays were developed to gain insight into the impacts of MnO x(s) age on bioavailability to Mn-reducing microorganisms and a quantitative polymerase chain reaction (qPCR) method was developed to quantify gene copies of the mtrB gene, which is involved in Mn-reduction. Results demonstrated that microbially-mediated Mn release was possible above a threshold equivalent of 2 × 10 2 S. oneidensis MR-1 CFU per gram of MnO x(s) coated media and that those organisms contributed to Mn desorption and release. Further, detectable mtrB gene copies were associated with observed Mn desorption. Lastly, MnO x(s) age appeared to play a role in Mn reduction and subsequent release, where MnO x(s) solids of greater age indicated lower bioavailability. These findings can help inform means of preventing soluble Mn release from drinking water treatment plant filters.

Organic buffers act as reductants of abiotic and biogenic manganese oxides

“…Mn oxides for use in biogeochemical studies 3,20,21 . While the biochemistry literature warned against the use of Good's buffers in the study of redox-sensitive processes more than two decades ago 17,18 , the environmental science community has been slow to adopt these findings 16,[22][23][24][25][26][27][28][29][30][31][32][33][34][35] . Myriad studies involving iron and manganese oxides have employed high Good's buffer concentrations (10-30 mM) [36][37][38][39][40][41] , although some recent studies have acknowledged buffer-induced reduction of metals [42][43][44][45][46][47] .…”