Abstract:As a result of high doses of paramagnetic gadolinium (Gd) chelates administered in magnetic resonance imaging (MRI) exams, their unmetabolized excretion, and insufficient removal in wastewater treatment plants (WWTPs), large amounts of anthropogenic Gd (Gdanth) are released into surface water. The upward trend of gadolinium-based contrast agent (Gd-CA) administrations is expected to continue growing and consequently higher and higher anthropogenic Gd concentrations are annually recorded in water resources, whi… Show more
“…Only two species of microalgae have been tested for the removal of the indigo blue (Spirulina platensis here and Scenedesmus quadricauda [15]). Both were able to achieve removals between 90% and 100%.…”
Section: Discussionmentioning
confidence: 99%
“…Nevertheless, recent progress has been made in an integrated perspective of wastewater treatment that includes standard and biological technologies for pharmaceutical emerging contaminants [4][5][6][7], industrial chemicals [8,9], brewery wastewater [10], agro-industrial wastewater [11,12], heavy metals [13,14], and emerging compounds [15].…”
Among the different chemical and physical treatments used to remove the color of the textile effluents, bioremediation offers many benefits to the environment. In this study, we determined the potential of Spirulina platensis (S. platensis) for decolorizing indigo blue dye under different incubation conditions. The microalgae were incubated at different pH (from 4 to 10) to calibrate for the optimal discoloration condition; a pH of 4 was found to be optimal. The biomass concentration in all experiments was 1 g/L, which was able to decolorize the indigo blue dye by day 3. These results showed that S. platensis is capable of removing indigo blue dye at low biomass. However, this was dependent on the treatment conditions, where temperature played the most crucial role. Two theoretical adsorption models, namely (1) a first-order model equation and (2) a second-order rate equation, were compared with observed adsorption vs. time curves for different initial concentrations (from 25 to 100 mg/L). The comparison between models showed similar accuracy and agreement with the experimental values. The observed adsorption isotherms for three temperatures (30, 40, and 50 °C) were plotted, showing fairly linear behavior in the measured range. The adsorption equilibrium isotherms were estimated, providing an initial description of the dye removal capacity of S. platensis.
“…Only two species of microalgae have been tested for the removal of the indigo blue (Spirulina platensis here and Scenedesmus quadricauda [15]). Both were able to achieve removals between 90% and 100%.…”
Section: Discussionmentioning
confidence: 99%
“…Nevertheless, recent progress has been made in an integrated perspective of wastewater treatment that includes standard and biological technologies for pharmaceutical emerging contaminants [4][5][6][7], industrial chemicals [8,9], brewery wastewater [10], agro-industrial wastewater [11,12], heavy metals [13,14], and emerging compounds [15].…”
Among the different chemical and physical treatments used to remove the color of the textile effluents, bioremediation offers many benefits to the environment. In this study, we determined the potential of Spirulina platensis (S. platensis) for decolorizing indigo blue dye under different incubation conditions. The microalgae were incubated at different pH (from 4 to 10) to calibrate for the optimal discoloration condition; a pH of 4 was found to be optimal. The biomass concentration in all experiments was 1 g/L, which was able to decolorize the indigo blue dye by day 3. These results showed that S. platensis is capable of removing indigo blue dye at low biomass. However, this was dependent on the treatment conditions, where temperature played the most crucial role. Two theoretical adsorption models, namely (1) a first-order model equation and (2) a second-order rate equation, were compared with observed adsorption vs. time curves for different initial concentrations (from 25 to 100 mg/L). The comparison between models showed similar accuracy and agreement with the experimental values. The observed adsorption isotherms for three temperatures (30, 40, and 50 °C) were plotted, showing fairly linear behavior in the measured range. The adsorption equilibrium isotherms were estimated, providing an initial description of the dye removal capacity of S. platensis.
“…[35][36][37] In recent years, utilization of high technology metals such as rare earth elements (REEs), whose abundance are extremely low in the earth, has rapidly increased with development of new types of industrial materials and pharmaceutical products. 38,39 In pollution may occur. Thus, we became interested in the research for a new type of potential anthropogenic pollution of high-technology metals with a focus on REEs in environmental water.…”
Section: Introductionmentioning
confidence: 99%
“…Eu and Tb. 15,39, This was artificially caused by anthropogenic sources mainly due to use of Gd compounds used as a contrast reagent for magnetic resonance imaging (MRI) in medical diagnosis.…”
Contents 1. Introduction 2. REEs in environmental water 2.1 Analytical methods 2.2 REE concentration anomalies 2.3 Comparison of the degree of Gd anomalies 2.4 Chemical speciation of Gd compounds 2.5 Ecotoxicology and bioavailability of anthropogenic REEs 3. Multielement analysis of high technology metals as well as REEs 4. Conclusion 5. Acknowledgements
“…Even if Gd is mainly transported as a dissolved fraction (Kulaksiz and Bau, 2013), according to Migaszewski and Gałuszka (2015) the origin and mechanisms of controlling the LREE, MREE, or HREE enrichment in soluble and solid fractions are still unknown. It is particularly unclear whether the REE patterns are linked to the aqueous processes or are related to the source of these elements (Ebrahimi and Barbieri, 2019). In recent reviews, Rogowska et al (2018) reported the scarcity of information on the level of Gd in aquatic sediments and the lack of any speciation analysis (China, Australia, Europe) and Migaszewski and Gałuszka et al (2015) highlighted the need to improve our knowledge about behaviour and origin of REE in the environment.…”
A B S T R A C TThe behaviour and sources of rare earth elements (REE) in river sediments were investigated at ten stations and two dams of the Tafna basin (Northern Algeria) during contrasting hydrological conditions and using a combination of normalisation procedures, REE anomalies, various REE ratios, and multivariate statistical analysis. The ranking and REE concentrations were in the range of other carbonated areas. The classical fractionation of the heavy REE(HREE) erosion pattern, evidenced from upstream to downstream by the La/Yb or Sm/Yb ratios, was disturbed by the presence of dams, which retained the light REE (LREE) in particular. The hydrological conditions, particle size, and geochemical characteristics controlled the REE patterns. The LREE were associated with clay minerals and HREE with coarse silts, whereas carbonate and particulate organic carbon (POC) did not influence the transport downstream. The total concentration of REE in sediments was not strongly affected by anthropogenic inputs from various sources (industrial activities, and domestic or medical wastes). Indeed, some LREE enrichment and anomalies were detected at a few stations and locally for Gd, Tb, and Yb. However, the anthropogenic contribution can partially be hidden by dilution due to particle erosion. High flow increased the LREE and MREE enrichment and LREE/HREE fractionation in some places due to erosion processes and anthropic influences (dam releases and local wastes inputs). Middle REE (MREE) and HREE were the most extractable elements unlike LREE (which are the most concentrated), particularly during high water conditions. Finally, the REE demonstrated the impact of natural processes (hydrological, geochemical, and physical) and some anthropogenic disturbances (waste inputs, fertilisers, and dams). This might inspire to develop such investigations in other similar semi-arid basins undergoing various pressures. The use of local bedrock as a reference and a set of geochemical and statistical tools, is recommended.
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