Abstract

PAHs are widely distributed in the environment and pose a serious threat to ecological security and human health. The P&A (Pseudomonas aeruginosa and Alcaligenes faecalis) bacterium consortium obtained in this study comes from oily sludge and is reused for the degradation of PAHs mixture in oily sludge. Few articles pay attention to the PAHs mixture in oily sludge and reuse the bacterium consortium for its degradation. The PAHs solution degradation efficient of P&A bacterial consortium under different environmental conditions, bioaugmentations, and exogenous stimulations were studied by ultraviolet visible spectrophotometer and gas chromatography–mass spectrometry. The result shows that, after 8 days of degradation under 35 °C, pH 7, with 5% (volume percent) of the inoculation amount, the degradation rate of NAP, PHE, and PYR solution could higher than 90%, 80%, and 70%, respectively. The additional crude oil could further improve the NAP, PHE, and PYR degradation efficiency. The minimum inhibitory concentration of Cu2+, Zn2+, and Pb2+ to bacterium were 2.002, 17.388, and 9.435 mM, respectively. The addition of surfactants had negative or limited positive effect on the PAHs degradation rate. Furthermore, the average degradation rates of NAP, PHE, and PYR, in oily sludge of local petroleum polluted area by P&A bacterial consortium, could all reach above 80%. Based on gas chromatography–mass spectrometry test results before and after incubation, P&A bacterial consortium also provides more opportunities for other organic compounds’ degradation.

Highlights

  • Introduction iationsPAHs, which are formed by direct connection, bending connection, or aggregation of multiple benzene rings [1,2,3], mainly occur during incomplete combustion [4] of fossil fuel, such as coal, oil, and gas, waste incineration sites, or the formation of crude oil [5,6], and are a class of compounds with genotoxicity, carcinogenicity, mutagenicity, and teratogenicity [7,8]

  • The medium was transferred into a 250 mL separating funnel, and petroleum ether and 1:1 H2 SO4 were added into separating funnel to completely integrate the crude oil into the organic phase

  • The two bacteria were from oily sludge, which shows the environmental adaptability of sludge, which shows the environmental adaptability of P&A bacterial consortium

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Summary

Materials

The NAP (naphthalene, analytical pure), PHE (phenanthrene 97 wt %), and PYR (pyrene 97 wt %) were purchased from local store. The crude oil (70.26% saturated hydrocarbon, 12.54% aromatic hydrocarbon, 7.38% asphaltene, and 9.82% gum) and oil sludge (oil content 5.62%, 0.2090 mg/g NAP, 3.1116 mg/g PHE, 1.00595 mg/g PYR, and organic compounds are mainly aromatic hydrocarbons) were collected from a local oil-polluted area in Shaanxi Province, China. GC-MS (7890B-5977B, Agilent Technologies Inc., Palo Alto, CA, USA), autoclave (LDZX-30KBS, Shanghai Shen’an Medical Instrument Factory, Shanghai, China), vortex turbidimeter (Vortex-2, Shanghai Hushi Industrial Co., Ltd., Shanghai, China), ultrasonic cleaner (KQ-100DE, Kunshan Ultrasonic Instrument Co., Ltd., Kunshan, China), bed temperature incubator (GTCS-2011, Changzhou Zhengrong Instrument Co., Ltd., Changzhou, China), biochemical incubator (SPX-250BIII, Tianjin taist Instrument Co., Ltd., Tianjin, China), UV-vis spectrophotometer (T2600, Shanghai Youke Instrument Co., Ltd., Shanghai, China), low-speed bench centrifuge

Basic Bacterium Information Test
GC-MS Operating Conditions
Quantitative Analysis of Single and Mixture PAHs
Quantitative Analysis of Crude Oil
PAHs Degradation Experiment
Optimization of PAHs
Degradation
Effect Analysis of Environmental Factors on Degradation
Effects
Crude Oil
Effect
Heavy Metal Ions
Bacteriostatic circles produced by different
Surfactants
Full Text
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