Composting of hPAH Contaminated Soil
Principal Investigators
James H. Johnson, Jr., Devasia V. Karimpanal, and Michael M. Gaines
Howard University
E-mail: jj@scs.howard.edu
Introduction
Recalcitrant organic compounds are such a major threat to the environment that
developing environmentally friendly and economically viable technology to cleanup
these contaminants is a top priority on today's research agenda. Though existing
technologies such as incineration are proven to destroy waste to a great extent,
disadvantages of high cost, environmental concerns, and public empathy often are
barriers to their utilization. Thus while developing alternative technologies
for contaminant cleanup, attention must be given to develop technologies that are
low cost and environmentally compatible.
Engineers and scientists at Howard University are reevaluating an age-old process
operating in nature to keep the biosphere clean and habitable. This process is
called composting. The Howard researchers, under the leadership of James H.
Johnson Jr., are trying to engineer the process of composting to enhance the
microbial degradation of targeted contaminants in a short period of time. The
success of this technology is dependent upon a suitable environment and
sufficient time for microbes to degrade even the most recalcitrant compounds.
Recent interest in exploring land farming for contaminated soil clean up is also
exploiting the inherent capacity of the microbes to breakdown the contaminants
into environmentally benign products.
The Research
Composting is a biological degradative process by which complex organic compounds
are converted to residuals and carbon dioxide and water. Why then are some
organic compounds left out while others are preferentially degraded? A basic
biological principle is in play here i. e. spend less to gain much. So microbes
go after energy sources (food) that could be broken down by expending the least
energy. Each organic compound has its own characteristics and behaves in a unique
way. If we can change the attribute of the bacteria or the attribute of the
organic compound, any type of compound could be degraded. By changing the
attribute of the bacteria, we engineer the bacteria which preferentially go after
the target compound that is to be degraded. By changing the attribute of the
compound, we make the compound behave like those easily degraded by the microbes.
A combination of the above two strategies can lead to successful bioremediation
of contaminated soil.
The model compound selected for the research is benzo(a)pyre (BaP), a
recalcitrant and carcinogenic polycyclic aromatic hydrocarbon (PAH). Bacteria
exposed to contaminants are shown to induce enzymes that degrade those specific
compounds. Experiments conducted in liquid media has shown that these bacteria
are capable of degrading BaP. To make use of this bacterial quality, bacteria are
isolated from PAH contaminated sites and used as inocula in the compost. Initial
experiments w ere to evaluate the behavior of BaP. Water solubility is a key
for bacteria to use any substance as a food source. Lack of bioavailability of
BaP was a major limitation that prevented the transport of BaP to bacterial cell.
Thus experiments were modified to overcome this limitation. One approach was to
use biological amendments such as composted sludge to enhance bacterial growth.
Soil binding of BaP also prevented mass transfer. This work has demonstrated the
ability of nonionic synthetic surfactants to mobilize BaP from soil.
The Results
Understanding barriers and limitations of BaP degradation and overcoming these
barriers were the focal points of Howard's research in developing composting
technology for PAH contaminated soil bioremediation. These studies showed that
mass transfer limitations and kinetic limitations prevent degradation of BaP.
When necessary steps were taken to overcome mass transfer limitation, BaP
degradation was achieved. Composting of soil without amendments did not result
in the degradation of BaP. On the other hand, BaP degradation was evident in
sludge amended soil. Sludge is a rich source of food for bacteria. Many
bacteria in nature are known to produce biological surfactants that in turn
enhances the solubility and transport of PAHs. Again, some of the organic
compounds also may have acted as cosubstrates thus aiding in the degradation of
BaP. Though Tween 80 , a nonionic surfactant at 6000 ppm was used with compost
amendment, there was no significant difference in the degradation of BaP in
sludge amended and sludge and surfactant amended soil. But in liquid
experiments, surfactants at 5000 ppm were found to enhance BaP degradation.
Higher concentrations of surfactants may enhance the degradation in soil
systems.
Future Research
The research at Howard generated an understanding of the major limiting factors
of BaP degradation and devised a workable strategy to overcome the limitations.
Both by manipulating bacterial growth conditions and enhancing the
bioavailability through surfactant addition, one of the most recalcitrant and
problem PAHs is successfully degraded under different laboratory conditions. The
next step is to try similar strategies on field contaminated soil and make
modifications, if needed, to pilot test the technology before field
demonstration.
Copyright © Georgia Tech Research Corporation, 1999.
All Rights
Reserved.
Make comments to: mark.hodges@gtri.gatech.edu
Last modified on: April 12, 1999.
URL: http://www.hsrc.org/