brine and ferric-chloride

brine has been researched along with ferric-chloride* in 4 studies

Other Studies

4 other study(ies) available for brine and ferric-chloride

ArticleYear
Potential of the integration of coagulation and ozonation as a pretreatment of reverse osmosis concentrate from coal gasification wastewater reclamation.
    Chemosphere, 2019, Volume: 222

    Combination of coagulation and ozonation was used to treat brine derived from a three-stage reverse osmosis (RO) process during coal gasification wastewater reclamation. Effects of operating parameters on the removals of total organic carbon (TOC), color and UV absorbance at 254 nm (A

    Topics: Carbon; Chlorides; Coal; Color; Ferric Compounds; Osmosis; Ozone; Salts; Waste Disposal, Fluid; Wastewater; Water Purification

2019
Surface complexation modeling of the removal of arsenic from ion-exchange waste brines with ferric chloride.
    Journal of hazardous materials, 2011, Apr-15, Volume: 188, Issue:1-3

    Brine disposal is a serious challenge of arsenic (V) removal from drinking water using ion-exchange (IX). Although arsenic removal with ferric chloride (FeCl(3)) from drinking waters is well documented, the application of FeCl(3) to remove arsenic (V) from brines has not been thoroughly investigated. In contrast to drinking water, IX brines contain high ionic strength, high alkalinity, and high arsenic concentrations; these factors are known to influence arsenic removal by FeCl(3). Surface complexation modeling and experimental coagulation tests were performed to investigate the influence of ionic strength, pH, Fe/As molar ratios, and alkalinity on the removal of arsenic from IX brines. The model prediction was in good agreement with the experimental data. Optimum pH range was found to be between 4.5 and 6.5. The arsenic removal efficiency slightly improved with higher ionic strength. The Fe/As ratios needed to treat brines were significantly lower than those used to treat drinking waters. For arsenic (V) concentrations typical in IX brines, Fe/As molar ratios varying from 1.3 to 1.7 were needed. Sludge solid concentrations varying from 2 to 18 mg L(-1) were found. The results of this research have direct application to the treatment of residual wastes brines containing arsenic.

    Topics: Arsenic; Chlorides; Ferric Compounds; Hydrogen-Ion Concentration; Ion Exchange; Models, Chemical; Osmolar Concentration; Salts; Surface Properties; Water Pollutants, Chemical

2011
Selective removal of arsenate from drinking water using a polymeric ligand exchanger.
    Water research, 2005, Volume: 39, Issue:20

    The new maximum contaminant level (MCL) of 10 microg/L for arsenic in the US drinking water will take effect on January 22, 2006. The compliance cost is estimated to be approximately dollar 600 million per year using current treatment technologies. This research aims to develop an innovative ion exchange process that may help water utilities comply with the new MCL in a more cost-effective manner. A polymeric ligand exchanger (PLE) was prepared by loading Cu2+ to a commercially available chelating ion exchange resin. Results from batch and column experiments indicated that the PLE offered unusually high selectivity for arsenate over other ubiquitous anions such as sulfate, bicarbonate and chloride. The average binary arsenate/sulfate separation factor for the PLE was determined to be 12, which were over two orders of magnitude greater than that (0.1-0.2) for commercial strong-base anion (SBA) exchangers. Because of the enhanced arsenate selectivity, the PLE was able to treat approximately 10 times more bed volumes (BVs) of water than commonly used SBA resins. The PLE can operate optimally in the neutral pH range (6.0-8.0). The exhausted PLE can be regenerated highly efficiently. More than 95% arsenate capacity can be recovered using approximately 22 BVs of 4% (w/w) NaCl at pH 9.1, and the regenerated PLE can be reused without any capacity drop. Upon treatment using FeCl3, the spent brine was recovered and reused for regeneration, which may cut down the regenerant need and reduces the volume of process waste residuals. The PLE can be used as a highly selective and reusable sorbent for removal of arsenate from drinking water.

    Topics: Arsenates; Chlorides; Copper; Ferric Compounds; Ion Exchange Resins; Salts; Water Pollutants, Chemical; Water Purification; Water Supply

2005
Treatment of spent brine from a nitrate exchange process using combined biological denitrification and sulfate precipitation.
    Water science and technology : a journal of the International Association on Water Pollution Research, 2004, Volume: 49, Issue:5-6

    A combined biological denitrification and sulfate precipitation process was developed to treat and reuse the spent brine produced by a nitrate exchange system. Although the spent brine contained a relatively high salt concentration, more than 80% of NO3(-)-N fed into the denitrification reactors was removed at a nitrate-N loading rate of 2.2 g NO3(-)-N/l x day, regardless of the presence or absence of sulfate up to 8,000 mg/l. Sulfate present in the spent brine was successfully removed by the addition of BaCl2 and the settling velocity of BaSO4 suspension was remarkably enhanced by FeCl3 coagulation. Since most of the chloride consumed in regenerating the exhausted resins was replaced during chemical treatment with BaCl2 and FeCl3, it was possible to reuse the treated spent brine as a regenerant after compensating for the small amount of unreplaced NaCl.

    Topics: Bioreactors; Chemical Precipitation; Chlorides; Conservation of Natural Resources; Ferric Compounds; Ion Exchange; Nitrates; Salts; Sulfates; Waste Disposal, Fluid

2004