38 research outputs found
Selective dissolution of eodiagenesis cements and its impact on the quality evolution of reservoirs in the Xing’anling Group, Suderte Oil Field, Hailar Basin, China
Phosphorus burial and diagenesis in the central Bering Sea (Bowers Ridge, IODP Site U1341): Perspectives on the marine P cycle
Etude expérimentale de la dissolution de l'apatite (impact sur le cycle biogéochimique dans le milieu naturel)
TOULOUSE3-BU Sciences (315552104) / SudocSudocFranceF
Surface characterization of natural apatites used to remove phosphates from wastewater in constructed wetlands: which techniques to use?
Phosphorus is an essential element for all life forms. However, an excessive
concentration of phosphates is the most common cause of water bodies eutrophication as
phosphorous is usually the limiting nutrient involved in plant growth. In constructed
wetlands (CWs) treating domestic wastewaters, good treatment performances are obtained on
main pollutants except with phosphates. In order to improve phosphate removal by CWs,
different experiments were performed considering a series of reactive substrates. Among
those, natural apatitic materials showed a high sorption capacity for phosphates. This
paper presents the various analytical techniques that were used to characterize five
natural apatitic materials which were tested in experiments performed at different scales
(laboratory, pilot plant and full-scale experiments). These apatitic materials have been
studied using X-ray powder diffraction, Raman spectroscopy and scanning electron
microscopy. In addition, chemical compositions were obtained from X-ray fluorescence and
ICP-MS analyses. The results suggest that the studied apatitic materials present a wide
spectrum of physical, mineralogical and chemical characteristics. This variety is related
to the presence of impurities in the natural materials (5–60% w/w). Therefore, the
characterization of the natural apatitic materials available is necessary in order to
select the ones that would lead to the best performances in terms of phosphate removal.
Moreover, the observation of the surface of the grains before and after the percolation of
phosphate containing solutions showed that the primary apatitic peloids were progressively
covered with a carbonate hydroxyapatite precipitate layer formed with the phosphates
removed from the treated solution
Rétention du phosphore par apatite en filtres plantés de roseaux : recommandations de dimensionnement
International audiencePhosphorus (P) removal in constructed wetlands (CWs) has received particular attention during the last decades by using specific materials which promote P adsorption/precipitation phenomena. Recent studies have shown an interest in using apatite materials to promote P precipitation onto their surface. About ten years of experiments at different scales (laboratory, pilot, full scale) have passed. The process is now open in France. This paper presents the first design recommendations according to the apatite mineral quality and treatment outlet requirements. Kinetics and their evolution with the material saturation degree are presented based on the k-C* model. The process can achieve 1 mgP.l-1 for long term while using surface P removal filter area of 0.5 m².p.e.-1. With a low land footprint and high P removal efficiency, the interest of the process also result in the orthophosphates accumulation on a phosphate mineral which makes easier to reuse phosphorus from wastewater once saturated
Rétention du phosphore par apatite en filtres plantés de roseaux : recommandations de dimensionnement
International audiencePhosphorus (P) removal in constructed wetlands (CWs) has received particular attention during the last decades by using specific materials which promote P adsorption/precipitation phenomena. Recent studies have shown an interest in using apatite materials to promote P precipitation onto their surface. About ten years of experiments at different scales (laboratory, pilot, full scale) have passed. The process is now open in France. This paper presents the first design recommendations according to the apatite mineral quality and treatment outlet requirements. Kinetics and their evolution with the material saturation degree are presented based on the k-C* model. The process can achieve 1 mgP.l-1 for long term while using surface P removal filter area of 0.5 m².p.e.-1. With a low land footprint and high P removal efficiency, the interest of the process also result in the orthophosphates accumulation on a phosphate mineral which makes easier to reuse phosphorus from wastewater once saturated
The dissolution kinetics and apparent solubility of natural apatite in closed reactors at temperatures from 5 to 50 degrees C and pH from 1 to 6
International audienc
Kinetics and mechanism of natural fluorapatite dissolution at 25 °C and pH from 3 to 12
International audienceThe dissolution rates of natural fluorapatite (FAP), Ca10(PO4)6F2, were measured at 25 °C in mixed-flow reactors as a function of pH from 3.0 to 11.7, and aqueous calcium, phosphorus, and fluoride concentration. After an initial preferential Ca and/or F release, stoichiometric Ca, P, and F release was observed. Measured FAP dissolution rates decrease with increasing pH at 3 ? pH ? 7, FAP dissolution rates are pH independent at 7 ? pH ? 10, and FAP dissolution rates again decrease with increasing pH at pH ? 10. Measured FAP dissolution rates are independent of aqueous Ca, P, and F concentration at pH ? 3 and pH ? 10. Apatite dissolution appears to be initiated by the relatively rapid removal from the near surface of F and the Ca located in the M1 sites, via proton for Ca exchange reactions. Dissolution rates are controlled by the destruction of this F and Ca depleted surface layer. The destruction of this layer is facilitated by the adsorption/penetration of protons into the surface at acidic conditions, and by surface hydration at neutral and basic conditions. Taking into account these two parallel mechanisms, measured fluorapatite forward dissolution rates can be accurately described using r(molms)=6.61×10aK1+aK+aCa4aF1.4aOH0.6aH6K+3.69×10[CaOH2+] where ai refers to the activity of the ith aqueous species, [CaOH2+] denotes the concentration of hydrated calcium sites at the surface of the leached layer (mol m?2), and Kex and Kads stand for the apparent stability constants of the Ca2+/H+ exchange and adsorption/penetration reactions, respectively
An experimental investigation of the effect of Bacillus megaterium on apatite dissolution
Kinetics and mechanism of natural fluorapatite dissolution at 25DC and pH from 3 to 12
International audienc