Microbial degradation and determination of polycyclic aromatic hydrocarbons
Many polycycic aromatic hydrocarbons (PAHs) are carcinogenic, and it is important to understand their fate in the environment. In this thesis, the microbial degradation of PAHs has been studied, with emphasis on the degradation of phenanthrene and pyrene. Several cultures were enriched from sea w...
Main Author: | |
---|---|
Format: | Others |
Language: | English |
Published: |
2009
|
Online Access: | http://hdl.handle.net/2429/8850 |
id |
ndltd-UBC-oai-circle.library.ubc.ca-2429-8850 |
---|---|
record_format |
oai_dc |
collection |
NDLTD |
language |
English |
format |
Others
|
sources |
NDLTD |
description |
Many polycycic aromatic hydrocarbons (PAHs) are carcinogenic, and it is
important to understand their fate in the environment. In this thesis, the microbial
degradation of PAHs has been studied, with emphasis on the degradation of phenanthrene
and pyrene. Several cultures were enriched from sea water and sediment samples obtained
from Kitimat Arm, B. C., an estuary environment that is contaminated by PAHs. It was
demonstrated that microorganisms in the cultures are able to degrade phenanthrene very
quickly and to utilize phenanthrene as the sole carbon and energy source. For example,
complete degradation of 100 mg of phenanthrene in 10 ml of medium is achieved 23 hr
after incubating phenanthrene with 0.5 ml of the culture and 10 ml of mineral salt medium
at ambient temperature. A strain (LY) that is capable of degrading phenanthrene was
isolated from a sea water culture and has been partially characterized.
Another sixteen mixed cultures prepared from Kitimat samples readily degraded
pyrene, in spite of the common perception that the microbial degradation of pyrene is very
difficult. Microorganisms in the cultures grew on pyrene, without any additional carbon
source. This is one of the few reports of microorganisms that can use pyrene as sole
carbon source. The possibility of complete break-down of pyrene was studied by
quantitatively measuring the amount of ¹⁴CO₂ produced from the mineralization of ¹⁴C-
labeled pyrene. Up to an estimated 45% of the ¹⁴C-labeled pyrene that was initially added
into the cultures was found to be mineralized to produce ¹⁴CO₂ and H₂O, after 12 days of
incubation. The rest of the ¹⁴C activity is primarily accounted for metabolites. A typical
metabolite, cis-4,5-dthydroxy-4,5-dihydropyrene, was identified in the cultures, by using
various chromatographic and spectrometric techniques developed during this study. This
metabolite was present in all the cultures catalyzing pyrene degradation and disappeared
only after pyrene was completely degraded. Therefore, there was the possibility that cis
4,5-dihydroxy-4,5-dihydropyrene could be used as an indicator for the in situ microbial degradation of pyrene in the Kitimat Arm environment: cis-4,5-dihydroxy-4,5-
dihydropyrene could be present because pyrene was continuously introduced to the
Kitimat environment and is constantly available to the microorganisms. Analysis of
environmental samples by using various analytical techniques showed that cis-4,5-
dihydroxy-4,5-dihydropyrene is indeed present in some near shore sediment and pore
water samples, in which a high concentration of pyrene is present. For the first time, these
studies showed strong evidence for the in situ degradation of pyrene in the natural
environment. Radioactive tracer studies using 14C-labeled pyrene also showed that
untreated sediment samples collected from Kitimat Arm can mineralize up to an estimated
28% of pyrene.
Two mixed cultures (Pysed-l and Pysed-2) were also tested for the ability to
degrade benzo(a)pyrene and a standard mixture of sixteen PAHs. Some important factors
influencing the degradation of these PAHs were studied, including temperature, the
composition of culture medium, the concentration of the PAHs, and the population of the
microorganisms. The degradation of pyrene at a temperature as low as 2 °C was observed.
The addition of peptone and yeast extract was found to enhance the degradation of PAHs.
Two methods were developed for the preconcentration of trace amounts of
organics in water samples, one based on the use of C₁₈ solid phase cartridges the other on
polytetrafluoroethylene tubing. === Science, Faculty of === Chemistry, Department of === Graduate |
author |
Li, Xing-fang |
spellingShingle |
Li, Xing-fang Microbial degradation and determination of polycyclic aromatic hydrocarbons |
author_facet |
Li, Xing-fang |
author_sort |
Li, Xing-fang |
title |
Microbial degradation and determination of polycyclic aromatic hydrocarbons |
title_short |
Microbial degradation and determination of polycyclic aromatic hydrocarbons |
title_full |
Microbial degradation and determination of polycyclic aromatic hydrocarbons |
title_fullStr |
Microbial degradation and determination of polycyclic aromatic hydrocarbons |
title_full_unstemmed |
Microbial degradation and determination of polycyclic aromatic hydrocarbons |
title_sort |
microbial degradation and determination of polycyclic aromatic hydrocarbons |
publishDate |
2009 |
url |
http://hdl.handle.net/2429/8850 |
work_keys_str_mv |
AT lixingfang microbialdegradationanddeterminationofpolycyclicaromatichydrocarbons |
_version_ |
1718588104692989952 |
spelling |
ndltd-UBC-oai-circle.library.ubc.ca-2429-88502018-01-05T17:34:25Z Microbial degradation and determination of polycyclic aromatic hydrocarbons Li, Xing-fang Many polycycic aromatic hydrocarbons (PAHs) are carcinogenic, and it is important to understand their fate in the environment. In this thesis, the microbial degradation of PAHs has been studied, with emphasis on the degradation of phenanthrene and pyrene. Several cultures were enriched from sea water and sediment samples obtained from Kitimat Arm, B. C., an estuary environment that is contaminated by PAHs. It was demonstrated that microorganisms in the cultures are able to degrade phenanthrene very quickly and to utilize phenanthrene as the sole carbon and energy source. For example, complete degradation of 100 mg of phenanthrene in 10 ml of medium is achieved 23 hr after incubating phenanthrene with 0.5 ml of the culture and 10 ml of mineral salt medium at ambient temperature. A strain (LY) that is capable of degrading phenanthrene was isolated from a sea water culture and has been partially characterized. Another sixteen mixed cultures prepared from Kitimat samples readily degraded pyrene, in spite of the common perception that the microbial degradation of pyrene is very difficult. Microorganisms in the cultures grew on pyrene, without any additional carbon source. This is one of the few reports of microorganisms that can use pyrene as sole carbon source. The possibility of complete break-down of pyrene was studied by quantitatively measuring the amount of ¹⁴CO₂ produced from the mineralization of ¹⁴C- labeled pyrene. Up to an estimated 45% of the ¹⁴C-labeled pyrene that was initially added into the cultures was found to be mineralized to produce ¹⁴CO₂ and H₂O, after 12 days of incubation. The rest of the ¹⁴C activity is primarily accounted for metabolites. A typical metabolite, cis-4,5-dthydroxy-4,5-dihydropyrene, was identified in the cultures, by using various chromatographic and spectrometric techniques developed during this study. This metabolite was present in all the cultures catalyzing pyrene degradation and disappeared only after pyrene was completely degraded. Therefore, there was the possibility that cis 4,5-dihydroxy-4,5-dihydropyrene could be used as an indicator for the in situ microbial degradation of pyrene in the Kitimat Arm environment: cis-4,5-dihydroxy-4,5- dihydropyrene could be present because pyrene was continuously introduced to the Kitimat environment and is constantly available to the microorganisms. Analysis of environmental samples by using various analytical techniques showed that cis-4,5- dihydroxy-4,5-dihydropyrene is indeed present in some near shore sediment and pore water samples, in which a high concentration of pyrene is present. For the first time, these studies showed strong evidence for the in situ degradation of pyrene in the natural environment. Radioactive tracer studies using 14C-labeled pyrene also showed that untreated sediment samples collected from Kitimat Arm can mineralize up to an estimated 28% of pyrene. Two mixed cultures (Pysed-l and Pysed-2) were also tested for the ability to degrade benzo(a)pyrene and a standard mixture of sixteen PAHs. Some important factors influencing the degradation of these PAHs were studied, including temperature, the composition of culture medium, the concentration of the PAHs, and the population of the microorganisms. The degradation of pyrene at a temperature as low as 2 °C was observed. The addition of peptone and yeast extract was found to enhance the degradation of PAHs. Two methods were developed for the preconcentration of trace amounts of organics in water samples, one based on the use of C₁₈ solid phase cartridges the other on polytetrafluoroethylene tubing. Science, Faculty of Chemistry, Department of Graduate 2009-06-05T22:31:24Z 2009-06-05T22:31:24Z 1994 1994-05 Text Thesis/Dissertation http://hdl.handle.net/2429/8850 eng For non-commercial purposes only, such as research, private study and education. Additional conditions apply, see Terms of Use https://open.library.ubc.ca/terms_of_use. 4245095 bytes application/pdf |