Azam, Shah Md. Golam Gousul (2015) Arsenic removal from contaminated waters by Fe-based (hydr)oxides and its phytoavailability in soil-plant system. [Tesi di dottorato]

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Item Type: Tesi di dottorato
Lingua: English
Title: Arsenic removal from contaminated waters by Fe-based (hydr)oxides and its phytoavailability in soil-plant system
Azam, Shah Md. Golam
Date: 30 March 2015
Number of Pages: 141
Institution: Università degli Studi di Napoli Federico II
Department: Agraria
Scuola di dottorato: Scienze agrarie e agroalimentari
Dottorato: Scienze delle risorse ambientali
Ciclo di dottorato: 27
Coordinatore del Corso di dottorato:
Rao, Maria
Mora, Maria de la LuzUNSPECIFIED
Date: 30 March 2015
Number of Pages: 141
Uncontrolled Keywords: As-contaminated waters, Fe-based (hydr)oxides, phytoavailability, As-stressed plants
Settori scientifico-disciplinari del MIUR: Area 07 - Scienze agrarie e veterinarie > AGR/13 - Chimica agraria
Aree tematiche (7° programma Quadro): AMBIENTE (INCLUSO CAMBIAMENTO CLIMATICO) > Proteggere i cittadini dai rischi ambientali
Date Deposited: 13 Apr 2015 12:57
Last Modified: 08 May 2016 01:00
DOI: 10.6092/UNINA/FEDOA/10120


Arsenic is considered as being synonymous with toxicity. Alarming As concentrations in natural waters is a worldwide problem. With greater public concern of As poisoning on human health, the developing regulatory guidelines and remediation technologies for mitigating As-contaminated ecosystems is an important issue. Urgent steps must be taken to reduce these impacts by providing access to safe water as a basic human right. Delaying mitigation is increasing death and disease. Layered double hydroxides (LDHs) show excellent capacity to sorb and exchange anions. Although arsenic (As) has a high affinity for sorbents containing Fe, only few studies have been carried out on the sorption of arsenite [As(III)] onto a Fe-based LDH. In this work we studied the sorption of As(III) onto a LDH containing Mg and Fe (Mg–Fe-LDH), as affected by: (i) pH; (ii) the presence of increasing concentrations of organic [citrate (CIT) and oxalate (OX)] and inorganic [phosphate (PO4), selenite (SeO3) and sulphate (SO4)] ligands, (iii) the effect of residence time on the desorption of As(III) by these ligands, and; (iv) the kinetics of desorption of As(III) by PO4. The As(III) sorption isotherms, carried out at different pHs, indicated a good affinity of the harmful oxyanion for the sorption sites of the Mg–Fe-LDH. This material was able to remove efficiently As(III) from contaminated solutions over a wide range of pH, but more in acidic than in alkaline systems. Competing ligands differently prevented the As(III) sorption on Mg–Fe-LDH, according to the following order: SO4 < OX << SeO3 < CIT < PO4. The desorption of As(III) by these anions decreased with increasing As(III) residence time on LDH surfaces. A comparison between the sorption/desorption of As(III) and As(V) on/from Mg–Fe-LDH in the presence or absence of anions highlights that less As(III) than As(V) is sorbed, whereas more As(III) than As(V) is desorbed by all the selected organic and inorganic ligands, but PO4. In recent decades, Fe-(hydr)oxides (e.g., Ferrihydrite and Goethite) have attracted substantial attention for their potential use as As sorbents. The aim of the work was to study the As(III) removal from contaminated waters by Fe-based minerals, by using Ferrihydrite [non-crystalline Fe-(hydr)oxide)] and Goethite [crystalline Fe-(hydr)oxide] as sorbent media in batch experiments. In particular, it was studied: i) the Langmuir isotherms of As(III) at pH 6.0; ii) arsenite sorption at different pHs; iii) arsenite sorption in presence of selected competing ligands, such as citrate (CIT), molybdate (MoO4), oxalate (OX), phosphate (PO4), selenite (SeO3), selenate (SeO4), and sulphate (SO4). Both Ferrihydrite and Goethite samples show a high affinity for As(III). However, the Ferrihydrite samples, characterized by a higher surface area (104.9 m2 g-1), were able to sorb much greater amounts of As(III) than the Goethite, with a lower surface area (42.3 m2 g-1). However, Ferrihydrite (Sm = 1245.1 mmol kg-1) adsorbed much more As(III) than Goethite (Sm = 327.9 mmol kg-1), essentially because of its greater surface area (178.2 vs. 42.3 m2 g-1) and, hence, lower degree of crystallinity, as well as to the greater affinity of As(III) for its surfaces. Probably, in our tests, Ferrihydrite adsorbed As(III) on their own external surfaces by forming a greater amounts of inner-sphere complexes vs. those formed by Goethite. The sorption of As(III) was lightly pH dependent. In fact, in the pH range of 4.0-9.0 the quantities of As(III) adsorbed resulted to be practically constant. The organic and inorganic ligands showed different capacities to compete with As(III) for the sorption sites of the Ferrihydrite and Goethite, according to the following increasing sequence: selenate< sulphate < oxalate < citrate < selenite ≈ molybdate< phosphate on Ferrihydrite, and sulphate ≈ selenate< oxalate < citrate <molybdate< selenite ≈ phosphate on Goethite. Carrot (Daucus carota L.) is widely consumed vegetable by humans. However, the study about influence of organic amendment (i.e. humic acid) and inorganic fertilizers (i.e. N, P, K) on As uptake, translocation, and its toxicity in carrot is limited. In this study carrot irrigated with different solutions containing As(III) and grown in a As-uncontaminated soil amended with increasing amounts of stabilized humic acid (half and full doses) and fertilized (half and full doses) with inorganic fertilizer. The aims of this experiment were to study: i) the influence of the humic acid application and inorganic fertilizer on the mobility and phyto-availability of As in soil; ii) the influence of the humic acids and inorganic fertilizer on the growth of the carrot plants and their uptake of As from contaminated systems. The carrot plants exposed to As showed typical phytotoxicity symptoms. Carrot plants growth was significantly affected by As and soil amended with humic acid and fertilization with inorganic fertilizer treatments. Carrot plants fertilized with inorganic fertilizer grew slightly more than those amended with commercial humic acids. Higher concentrations of As were found in carrot tissues when plants were irrigated with increasing levels of As. Most of the As taken up by edibleroots, while a lesser allocation of toxicant occurring in leaf biomass. In comparison to unfertilized control, plants amended with organic fertilizer exhibited a lower concentration of As in their own tissues, while the opposite was happened in fertilized with inorganic fertilizer. Here we observed the concentration of free-fraction As in soil samples after the amendment by humic acid and fertilization by inorganic fertilizer treatment. In soil, amended with humic acids and irrigated with As-contaminated water, there was a significant decrease of the nonspecifically sorbed As fraction and a contemporary increase of the specifically sorbed As fraction. This trend was due to partial immobilization of the As by the organic functional groups, either directly or through cation bridging. On the other hand, the fertilization with inorganic fertilizer determined a slight increase of the nonspecifically sorbed As and a consequent decrease of the specifically sorbed As. Hence, the addition of humic acid to soils could be used as an effective means to limit As accumulation in crops from As-contaminated waters.


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