2022
DOI: 10.3390/ma15103540
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Characteristics of the Properties of Absodan Plus Sorbent and Its Ability to Remove Phosphates and Chromates from Aqueous Solutions

Abstract: The aim of the research was to characterize the parameters of the diatomite sorbent Absodan Plus as well as to assess its suitability for the adsorption of chromates and phosphates from acidic aqueous solutions simulating the conditions occurring in some types of industrial wastewater. The scope of the research includes XRD, SEM, BET, and PZC analyses, and 3D observation of commercial diatomite granules and batch tests to determine the constants of kinetics and the equilibrium of chromates and phosphates adsor… Show more

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Cited by 5 publications
(6 citation statements)
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“…The final phase is the establishment of an equilibrium. The unusual nature of the binding process may be caused by limiting factors, such as the specific structure of the adsorbent, the solution, and its ions [ 97 ].…”
Section: Resultsmentioning
confidence: 99%
See 1 more Smart Citation
“…The final phase is the establishment of an equilibrium. The unusual nature of the binding process may be caused by limiting factors, such as the specific structure of the adsorbent, the solution, and its ions [ 97 ].…”
Section: Resultsmentioning
confidence: 99%
“…In the studies conducted so far on the kinetics of reactive materials, the most frequently fitted kinetic model was the pseudo-second-order model proposed by Ho, which assumes that the rate-limiting step of the process most likely involves chemical interactions leading to the binding of metal ions or organic compounds on the adsorbent surface via the mechanism (among others) of ion exchange or complexation [ 25 ]. The tested sorbents showed the best fit in terms of phosphorus binding to this model via the value of the determination coefficient (R 2 ): diatomite (0.99), zeolite (0.97), hydrotalcite (0.98), activated alumina (0.99) [ 78 ], hydroxy-aluminum pillared bentonite (1.00), hydroxy-iron pillared bentonite (0.99), mixed hydroxy-iron–aluminum pillared bentonite (1.00) [ 98 ], akadama clay (0.99), acid-activated akadama clay (0.99) [ 47 ], thermally modified zeolite (0.99) [ 99 ], Absodan Plus ® (0.99) [ 97 ], and Tunisian activated clays (0.99) [ 31 ]. A special case was calcium-rich sepiolite, which was characterized by fitting both to the pseudo-first and pseudo-second order kinetics models, which may indicate chemical sorption with valence forces via sharing, i.e., electron exchange between the adsorbent and the adsorbate [ 54 ].…”
Section: Resultsmentioning
confidence: 99%
“…Freundlich: q e = K F C e 1/n (6) where q e (mg/g) is the equilibrium adsorption amount, K L (L/mg) is the Langmuir adsorption equilibrium constant, q max (mg/g) represents the maximum adsorption capacity, C e (mg/L) represents the P equilibrium concentration, K F (mg (1−1/n) L 1/n /g) represents the Freundlich adsorption constant representing the adsorption capacity of the adsorbent materials, and n represents an indication of linearity. The fitted adsorption isotherms of P onto the E-C adsorbent materials are shown in Figure 2.…”
Section: Adsorption Isothermsmentioning
confidence: 99%
“…Different biological, chemical, and physical techniques have been created and widely applied in previous studies to manage and treat the phosphorus (P) present in wastewater [5,6]. Among these methods, the adsorption method is the most attractive since it is economically feasible and simple in real application.…”
Section: Introductionmentioning
confidence: 99%
“…The maximum permissible concentration of chromium in drinking water recommended by the World Health Organization (WHO) is 0.05 ppm. Chromium-containing wastewater is treated using chemical precipitation and coagulation [ 2 , 3 ], electrocoagulation [ 4 , 5 ], electroreduction and membrane separation [ 6 ], ion exchange [ 7 ], and sorption methods [ 8 , 9 , 10 , 11 , 12 ].…”
Section: Introductionmentioning
confidence: 99%