Phytoremediation of industrial sludge using vegetation‐assisted dewatering

With the emergence of risk‐based corrective action decisions, there is interest in the use of more natural techniques that may be as protective as the traditional removal, landfill, or capping approaches for impoundment closure. The use of phytoremediation is one of the more promising techniques. This article presents the results of a three‐year field‐pilot phytoremediation study that involved the use of plants to enhance sludge dewatering at an inactive natural gas‐cracking wastewater lagoon. The dewatering was accompanied by contaminant reduction of benzene, toluene, xylene (BTX), and naphthalene concentrations to below the cleanup goals. Meanwhile, the concentration reductions of three or more ring polynuclear aromatic hydrocarbons (PAHs) varied between 30 percent and 60 percent, except for dibenz[a,h]anthracene. The residual PAHs in the sludge are not leaching. Parallel laboratory studies suggest a reduced PAH availability and mobility in the unsaturated zone sludge. © 2002 Wiley Periodicals, Inc.     

Bioconcentration and biokinetics of heavy metals in the earthworm

This study examines the steady state and non-steady state kinetics of five metals, cadmium, copper, lead, nickel, and zinc in earthworms. The steady state kinetics are based on field studies in which worms from contaminated and uncontaminated sites were collected and measurements were made of concentrations in the earthworms and soils. For each of the metals, evidence suggests that bioconcentration depends on the metal concentrations in the soil; bioconcentration is greater at lower soil concentrations. The studies of non-steady state kinetics involve uptake and elimination experiments in which worms are transferred from an uncontaminated soil to a contaminated soil (uptake studies) or from a contaminated soil to an uncontaminated soil (elimination studies). The voiding time is shown to be an important experimental variable in determining the measured levels of metal in earthworms because experimental measurements are usually made on a worm-soil complex (i.e. the soft tissue of the worm and the soil in the gut of the worm). Thus, for metals that are bioconcentrated in worm tissue, increasing the voiding period increases the concentration of the metal in the worm-soil complex. Conversely, for metals that are not bioconcentrated, increasing the voiding time leads to a decrease in concentrations in the worm-soil complex.     

Effect of Periods of Non-Use on Biofilter Performance

Abstract

A biofilter does not operate as a true filter, but removes chemicals from gases by sorption and biologically degrades them. The objective of the research reported in this paper was to investigate the effect of periods of non-use on biofilter performance. The concept of non-use had two meanings in this research: "no chemical loading," which indicated that humidified air was passing through the biofilter with no chemicals, and "stagnant," which reflected that no flow at all was passing through the biofilter. Both instances of nonuse can require the microorganisms in the biofilter to reacclimate to differences in loading and type of chemical when a chemical load is re-applied. Acclimation time was compared with three different chemicals, initial acclimation was compared with re-acclimation following different periods of non-use, and the effect of humidification during the period of non-use was examined.

Bench scale testing produced results indicating that acclimation times ranged from several hours to longer than a day. Longer periods of biofilter non-use resulted in longer reacclimation periods and transition between different chemicals resulted in acclimation periods shorter than initial acclimation periods. Stagnant periods produced longer re-acclimation periods than periods of no chemical loading.