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Suzelle F Barrington

Publications and source records attributed to Suzelle F Barrington.

2 recordsLinked to original sources

Effect of surfactant alkyl chain length on soil cadmium desorption using surfactant/ligand systems.

The effect of surfactant alkyl chain length on soil Cd desorption was studied using nonionic surfactants of polyethylene oxide (PEO) of PEO chain lengths of 7.5 (Triton X-114), 9.5 (Triton X-100), 30 (Triton X-305), or 40 units (Triton X-405) in combination with the I- ligand. Triplicate 1 g soil samples were equilibrated with 15 ml of surfactant-ligand mixture, at concentrations of 0.025, 0.50 or 0.10, and 0.0, 0.168 or 0.336 mol/l, respectively. After shaking the samples for 24 h, the supernatant fraction was analyzed for Cd content to determine the percent of Cd desorbed from the soil. After five successive washings, 53%, 40% and 25% of Cd had been desorbed by 0.025, 0.050 or 0.10 mol/l of Triton X-114, respectively, in the presence of 0.336 mol/l of I-, whereas with the same conditions, Triton X-100 desorbed 61%, 57% and 56% Cd and either Triton X-305 or Triton X-405 desorbed 51, 40 and 14 to 16% Cd. The most efficient Cd desorption was obtained using 0.025 mol/l Triton X-100 in admixture with 0.336 mol/l I-. Increased surfactant concentration was detrimental to Cd desorption consistent with a process that blocked ligand access to the soil particle surface. After 5 washings,the cumulative cadmium desorption decreased with increasing surfactant alkyl chain length, indicating that the metal-ligand complexes are preferably stabilized by the micelles' hydrophobic octyl phenyl (OP) group rather than by the hydrophilic PEO group. In the absence of ligand, the surfactants alone desorbed less than 1% Cd from the contaminated soil, suggesting that the ligand, rather than the surfactant, extracts the metal, to be subsequently stabilized within the surfactant micelles.

Cadmium↗

Simultaneous soil Cd and PCB decontamination using a surfactant/ligand solution.

The simultaneous desorption of Cd and PCBs, from a contaminated soil, was investigated using a surfactant/ligand solution. The test surfactants were combinations of a nonionic surfactant [polyethylene oxide (PEO) of chain length 7.5 (Triton X-114), 9.5 (Triton X-100), 30 (Triton X-305), or 40 units (Triton X-405)], with iodide (I-). Triplicate 1 g soil samples were equilibrated, during 24h, with 15 mL of surfactant/ligand solution, at 0.025 or 0.50 and 0.0, 0.168, or 0.336 mol L(-1), respectively. The supernatant fraction was then separated from the particulates by centrifugation and analyzed for Cd to determine Cd desorption efficiency. After five consecutive washings, the treated soil samples were analyzed for PCB content to determine the desorption efficiency of this class of toxicant. Desorption of Cd increased with both increasing ligand concentration and decreasing surfactant chain length and concentration. The maximum Cd desorption efficiency (61%), was obtained with Triton X-100 at 0.025 mol L(-1), in the presence of I at 0.336 mol L(-1). After 5 successive washings, virtually quantitative PCB desorption (below limits of detection for tetra-, penta-, and hexachloro biphenyl compounds) had been achieved with most of surfactant/ligand combinations. Maximum desorption efficiency was achieved using either shorter chain length surfactant (n = 7.5 or 9.5) in combination with a higher ligand concentration, or using longer chain length surfactants (n = 30 and 40) with a lower ligand concentration. Thus, heavy metals and PCBs can be desorbed simultaneously from a contaminated soil with the same washing reagents, namely a surfactant-ligand combination. The optimum surfactant-ligand combination for the simultaneous desorption of both heavy metals and PCBs was a short chain length (n = 7.5 or 9.5) surfactant at low concentration admixed with 0.336 mol L(-1) I-.

Adsorption↗