Need for remediation
Decades of manufacturing and industrial development have left worldwide many lands ecologically degraded and contaminated with a vast array of organic and inorganic chemicals. These lands are mainly found at old industrial and commercial sites. In addition to such lands, soils have been also contaminated with hydrocarbons such as petroleum residues, solvents, pesticides, herbicides, wood preservatives, munition such as TNT, etc.
There are presently two main strategies for accomplishing soil decontamination: physical decontamination and bioremediation.
Physical decontamination is conducted using techniques such as soil washing and soil vapor extraction and can be used on a variety of both organic and inorganic toxins. Such strategies however have high costs, are conducted ex situ (excavating the soil and treating it batchwise in a surface mixer, leach pile, etc.), resulting in greater site disturbance and require de-toxification or immobilization of contaminants that were in the soil and after decontamination are present in solvents or other soil cleansing materials. Furthermore, physical decontamination methods are not effective for DNAPLs (Dense Nonaquaeous-Phase Liquids) such as petroleum residues.
Bioremediation on the other hand is a lengthy process and is difficult to monitor and control. Such strategies present inconsistent results associated with toxicity, biodegradability, solubility and nutrient availability. Even though biotreatment is lower cost than conventional methods, can be conducted in situ (treating the soil in place using sprayers, sprinklers or nozzle injectors) and eliminates the need to de-toxify or dispose of contaminated solvents or other cleansing materials, it has limited application for sites contaminated with metals or other inorganics.
Other strategies such as landfilling and incineration have major shortcomings as well, since landfilling decreases the availability of suitable disposal sites and increases transportation and disposal costs, while incineration involves a lengthy and difficult permitting process and high capital costs.
Humic acids based products are ideally suited
Humic acids , offer a cost effective, organic and simple way of remediating degraded and contaminated soils. Humic acids are nontoxic and biodegrade slowly. They have low oxygen demand and have excellent fixation and adsorption properties for xenobiotics in soil.
Apart from this, dissolved humic acids can be used in improving DNAPL (Dense Nonaqueous-Phase Liquids) mobilization and solubilization. Chlorinated solvent concentration is widespread across many energy and industrial complexes. DNAPLs, when not removed completely, present a long-term source of groundwater contamination.
When DNAPLs occur in the subsurface, they resist remediation due to their low water solubility, high viscosity and interfacial tension. Surfactants have been used with some success to improve the solubility of DNAPLs, however they are expensive and toxic and exhibit an oxygen demand. An alternative for enhancing DNAPL remediation is the use of dissolved humic acids, which have excellent mobilization properties for chlorinated solvents, and can be applied to improve several existing technologies such as pump-and-treat.
Use of Humid Acid Solution to Remove Organic Contaminants from Hydrogeologic Systems
Abdul S. Abdul • Thomas L. Gibson • Devi N. Rai
Experiments were carried out to evaluate the effectiveness of a 29 mg/L solution of humic acid to enhance the removal of six aromatic hydrocarbons (benzene, toluene, p-xylene, ethyltoluene, sec-butylbenzene, and tetramethylbenzene) from a sandy material. None of the compounds were completely removed from the material. Nonetheless, the compounds with the highest water solubility, benzene and toluene, were removed effectively; less than 1 mass % was retained with use of either the humic acid solution or water. For the less soluble organic compounds, removal was more difficult and was enhanced by the humic acid solution compared to water. Mass percent retained with humic acid was as follows: p-xylene, 1.4% (24% less than water); 3-ethyltoluene, 6.4% (40% less); sec-butylbenzene, 39% (14% less); and tetramethylbenzene, 43% (14% less).
The positive effect of humic acid on the removal of these organicsThe positive effect of humic acid on the removal of these organics may arise from the aggregation of the humic acid molecules to form membranes and/or micelles, having hydrophilic exteriors and hydrophobic interiors. may arise from the aggregation of the humic acid molecules to form membranes and/or micelles, having hydrophilic exteriors and hydrophobic interiors. Partitioning of the hydrophobic organics from the bulk solution into the hydrophobic interior of these humic acid structures can account for their enhanced removal from the sandy material.