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Hydrochars produced from different feedstocks (sawdust, wheat straw, and corn stalk) via hydrothermal carbonization (HTC) and KOH modification were used as alternative adsorbents for aqueous heavy metals remediation. The chemical and physical properties of the hydrochars and KOH-treated hydrochars were characterized, and the ability of hydrochars for removal of heavy metals from aqueous solutions as a function of reaction time, pH, and initial contaminant concentration was tested. The results showed that KOH modification of hydrochars might have increased the aromatic and oxygen-containing functional groups, such as carboxyl groups, resulting in about 2-3 times increase of cadmium sorption capacity (30.40-40.78 mg/g) compared to that of unmodified hydrochars (13.92-14.52 mg/g). The sorption ability among different feedstocks after modification was as the following: sawdust > wheat straw > corn stack. Cadmium sorption kinetics on modified hydrochars could be interpreted with a pseudo-second order, and sorption isotherm was simulated with Langmuir adsorption model. High cadmium uptake on modified hydrochars was observed over the pH range of 4.0-8.0, while for other heavy metals (Pb, Cu, and Zn) the range was 4.0-6.0. In a multi-metal system, the sorption capacity of heavy metals by modified hydrochars was also higher than that by unmodified ones and followed the order of Pb(II) > Cu(II) > Cd(II) > Zn(II). The results suggest that KOH-modified hydrochars can be used as a low cost, environmental-friendly, and effective adsorbent for heavy metal removal from aqueous solutions. [ABSTRACT FROM AUTHOR]

We prepared and tested carboxymethyl-cellulose-bridged nano-chlorapatite (CMC-CAP) for simultaneous immobilization of Pb, Zn, Cu, and Cd in a field-contaminated acidic soil. Amending the field-contaminated soil using 0.5 wt.% CMC-CAP and 0.1 wt.% CaO was most effective in immobilizing the four metals, which decreased the leachabilities by 98.2%, 98.3%, 96.3%, and 96.2% for Pb, Zn, Cu, and Cd, respectively, after 1 day of treatment. The acid-leached metals fluctuated in the first 60 days, and then approached to steady state after 180 days, where the acid-leachable concentrations all met the regulation levels, and the immobilization was further consolidated when further aged for 365 days. Column elution tests showed that the soil amendment lowered the peak metal concentrations by > 92.5%, and the total eluted masses by >71.9%. Sequential extraction revealed that the soil amendment converted the exchangeable fractions to the much less available Fe-Mn oxides bound and residual forms, and thus, lowered the risk levels to "low risk" for all the metals. The immobilization of the metals was facilitated through formation of stable metal (chloro)phosphates, surface complexation, and/or ion exchange reactions. Combined CMC-CAP and CaO may serve as an effective formulation for simultaneous and long-term immobilization of multiple heavy metals in acidic soil. ga1 • Carboxymethyl cellulose bridged chlorapatite (CMC-CAP) was prepared and tested. • CMC-CAP + CaO effectively immobilized Pb, Zn, Cu and Cd in a field acidic soil. • Aging the amended soil for 365 days consolidated the immobilization of the metals. • The immobilized metals remained stable under 1440 pore volumes of acid rain elution. • Precipitation, surface complexation, and ion exchange are key mechanisms. [ABSTRACT FROM AUTHOR]

• CMC-stabilized FeS nanoparticles offer faster sorption rate and greater uptake for Cd than bare FeS. • Surface complexation and chemical precipitation are dominant immobilization mechanisms. • Dual-mode model well interprets Cd sorption isotherm with a Q max of 497.5 mg/g. • CMC-FeS performs well at typical natural water chemistry conditions (pH, humic acid, and oxygen). • Immobilized Cd remains stable without remobilization over prolonged periods. Cadmium (Cd) is one of the most commonly detected toxic heavy metals in the environment. Ferrous sulfide (FeS) nanoparticles were prepared using sodium carboxymethyl cellulose (CMC) as a stabilizer and tested for removal of Cd from aqueous solutions. Effects of CMC concentration, initial Cd concentration, pH, humic acid (HA) and dissolved oxygen were examined. Fully stabilized FeS (100 mg/L) nanoparticles were obtained using 0.01 wt% CMC. Batch kinetic tests showed that the nanoparticles at 100 mg/L as FeS rapidly removed 93% of 1 mg/L Cd within 4 h at pH 7.0, and the kinetic data were well interpreted by a pseudo-second-order rate model with a rate constant of 6.68 g·mg−1·hr−1. Sorption isotherm was well simulated by a dual-mode isotherm model with a maximum Langmuir sorption capacity of 497.5 mg/L at pH 7.0. Fourier transform infrared (FTIR) spectroscopy and X-ray powder diffraction (XRD) analyses suggested that chemical precipitation and surface complexation between Cd and FeS were dominant immobilization mechanisms. Increasing pH from 4.0 to 8.0 enhanced Cd removal rate from 73.0% to 98.8%, whereas addition of 3 mg/L HA (as total organic matter) inhibited the removal rate by 2.7% and the presence of molecular oxygen had negligible effect. Increasing NaCl or CaCl 2 from 0 to 10 mM suppressed Cd removal by 10.1% and 27.7%, respectively. The immobilized Cd remained insoluble when aged for 717 days under anoxic or oxic conditions. This study demonstrated that CMC-stabilized FeS nanoparticles can facilitate long-term immobilization of cadmium in contaminated water. [ABSTRACT FROM AUTHOR]

Soil contamination by heavy metals and metalloids has been a major environmental challenge. While various remediation technologies have been reported, field data on the remediation effectiveness have been limited. We tested a new remediation technology for on-site immobilization of As(III) and Pb(II) in a contaminated soil at an abandoned chemical plant site. A novel ternary amending agent consisting of Fe 2 O 3 , MnO 2 , and Mg(OH) 2 (molar ratio = 1.0:5.5:5.5) was used to amend the soil on-site. Field monitoring data indicated that the amendment severed as a pH buffer and a long-term sequester for both As and Pb in the soil. At a dosage of 3 wt%, the acid-leachable As and Pb were lowered from 0.042–0.077 mg/L and 0.013–0.022 mg/L to 0.0062–0.0093 mg/L and 0.0030–0.0080 mg/L, respectively, after one day of the amendment, and to 0.0020–0.0050 mg/L and 0.0020–0.0054 mg/L after 240 days of aging. As(III) was oxidized to As(V) and subsequently immobilized via complexation and precipitation, whereas Pb(II) was sequestered via electrostatic attraction and chemical precipitation. The treatment cost was estimated at $31.5/m3. The results indicate that complex contaminants in soil can be effectively immobilized using combined amending agents that can interact with the target chemicals and induce synergistic immobilization reactions. [Display omitted] • A cost-effective soil amendment Fe-Mn-Mg(OH) 2 was prepared for field applications. • The amendment effectively immobilized As and Pb at a former chemical plant site. • Immobilization of As and Pb was enhanced when aged for 240 d under field conditions. • As(III) was oxidized to As(V) and stabilized via complexation and precipitation. • Pb(II) was immobilized via electrostatic interaction and chemical precipitation. [ABSTRACT FROM AUTHOR]