A Na–smectite clay (Na–SWy-2) was exchanged with various amounts of dimethyldioctadecylammonium bromide (DODA-Br) up to twice the cation exchange capacity (CEC). The organoclay (DODA–SWy-2) with DODA-Br added at 2 × CEC exhibited a maximum 4.2 nm d-spacing and a 31.4% carbon content, which demonstrates DODA+ intercalation. DODA–SWy-2 was evaluated as an archetype of commercial products used to sequester hydrophobic contaminants, and the nature of the primarily C18 alkylhydrocarbon-chain interlayer environment was emhasized. Shifts in ν(CH) and CH2 rocking band positions in DODA–SWy-2-complex FTIR-spectra indicate that DODA C18 chains were more ordered as DODA surface coverage was increased. Differential scanning calorimetry analysis indicated a DODA–SWy-2 gel-to-liquid transition temperature much lower than the melting point of crystalline DODA-Br and similar to that of aqueous DODA-Br vesicles. This suggests that the transition was governed by C18 alkyl tail–tail interactions in the clay interlamellar region. Dibenzo-p-dioxin (DD) sorption from water by DODA–SWy-2 was compared to DD sorption by the geosorbents granular activated carbon (GAC), K-exchanged saponite, and a muck soil. The linear Kl sorption coefficients (log Kl) from a linear fit of the sorption isotherms were 4.37 for DODA–SWy-2, 5.55 for GAC, 3.19 for muck soil, and 2.46 for K-saponite. The DD-organic-matter-normalized sorption coefficient (Kom) was ~2.4 times the octanol–water partition coefficient (Kow). This indicates that DD has a higher affinity for the nonpolar interlayer DODA organic phase than for octanol. In contrast, the Kom for muck soil DD sorption was ~10 times less than Kow, which reflects the higher polarity of amorphous soil organic matter relative to octanol. Enhanced DD uptake by the DODA-derived lipophilic phase in the organoclay is attributed to the low polarity, “open” C18 alkyl structure due to the physical dimensions of “v-shaped” DODA+ molecular, and low density of the interlamellar phase (~0.50 g/ cm3) density of intercalated DODA+.
The findings of recent research and evaluation efforts are assessed to determine whether solidification/stabilization (S/S) has been properly and appropriately applied for different types of hazardous wastes. Results from these studies are mixed and, as a result, the need for proper test procedures and for treatability studies is emphasized. Technical guidance is given for assessing the appropriateness of using S/S for any specific wastes.
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