- Original article
- Open Access
Effect of high pressure on hydrocarbon-degrading bacteria
AMB Express volume 4, Article number: 77 (2014)
The blowout of the Deepwater Horizon in the Gulf of Mexico in 2010 occurred at a depth of 1500 m, corresponding to a hydrostatic pressure of 15 MPa. Up to now, knowledge about the impact of high pressure on oil-degrading bacteria has been scarce. To investigate how the biodegradation of crude oil and its components is influenced by high pressures, like those in deep-sea environments, hydrocarbon degradation and growth of two model strains were studied in high-pressure reactors. The alkane-degrading strain Rhodococcus qingshengii TUHH-12 grew well on n-hexadecane at 15 MPa at a rate of 0.16 h−1, although slightly slower than at ambient pressure (0.36 h−1). In contrast, the growth of the aromatic hydrocarbon degrading strain Sphingobium yanoikuyae B1 was highly affected by elevated pressures. Pressures of up to 8.8 MPa had little effect on growth of this strain. However, above this pressure growth decreased and at 12 MPa or more no more growth was observed. Nevertheless, S. yanoikuyae continued to convert naphthalene at pressure >12 MPa, although at a lower rate than at 0.1 MPa. This suggests that certain metabolic functions of this bacterium were inhibited by pressure to a greater extent than the enzymes responsible for naphthalene degradation. These results show that high pressure has a strong influence on the biodegradation of crude oil components and that, contrary to previous assumptions, the role of pressure cannot be discounted when estimating the biodegradation and ultimate fate of deep-sea oil releases such as the Deepwater Horizon event.
From April to July 2010, 779 million litres of oil were released into the Gulf of Mexico when the Deepwater Horizon (DWH) drilling rig platform exploded (Atlas and Hazen ). This event was the largest marine oil spill in history. However, there are other anthropogenic and natural sources of oil released into the oceans. The National Research Council () estimated an overall input of about 1.3 Mt oil per year into the marine environment from all sources. Approximately 47% originates from natural seeps and the remaining 53% comes from activities related to the extraction, transportation and consumption of crude oil or refined products (National Research Council ).
In case of the Deepwater Horizon accident, it is estimated that a substantial proportion of the hydrocarbons entering deep plumes was converted to biomass (about 0.8–2· 1010 mol carbon) (Shiller and Joung ). Substantial bacterial blooms were observed in deep waters in the months following the blowout, indicating that indigenous hydrocarbon-degrading bacteria were enriched by the released crude oil and methane (Bælum et al.; Hazen et al.; Kessler et al.; Redmond and Valentine ; Valentine et al., ). Oil-degrading bacteria have evolved over millions of years and are ubiquitous in the marine environment. Up to now, more than 200 bacterial, algal and fungal genera, representing over 500 species, are described as capable of hydrocarbon degradation (Yakimov et al.). Therefore, natural bacterial activity is an important mechanism for environmental remediation of oil spills. Much research has been done on crude oil biodegradation in the marine environment (e.g. Colwell et al.; Head et al. ; Leahy and Colwell ; Powell et al. ; Yakimov et al.), especially in the context of the DWH blowout (Hazen et al. ; Kessler et al.; Redmond and Valentine ; Valentine et al. ).
The DWH drilling rig well, from which oil and gas flowed out uncontrollably for three months, was located 1,500 m below the sea surface. Such deep-sea environments are characterized by extreme conditions. These include low temperatures of 3°C (±1°C) (Jannasch and Taylor ) and high hydrostatic pressures up to 110 MPa in the Mariana Trench, the deepest site existing in the ocean at 10,994 m (±40 m) (Abe and Horikoshi ; Gardner and Armstrong ). However, only a limited number of studies regarding the capabilities of bacteria to degrade oil and hydrocarbons have been conducted under high pressure (Grossi et al. ). Despite the detection of pressure-induced differences in growth and hydrocarbon utilisation (Schwarz et al., ), most reports have investigated oil biodegradation only at surface pressure (0.1 MPa) (Cui et al. ; Tapilatu et al.; Wang et al.), and corresponding results may not be applicable to the deep sea. Thus, oil biodegradation processes under extreme deep-water conditions are not well understood. Although the rate and extent of hydrocarbon degradation at elevated pressures has been understudied, an understanding of the impact of elevated pressures on biodegradation is increasingly critical in the wake of expanding drilling in deep waters.
This study aims to improve our understanding of microbial degradation processes of crude oil at in situ deep-sea conditions. In particular, we consider the effects of high pressure on hydrocarbon biodegradation using high-pressure lab technology. Oil is one of the most complex mixtures of organic compounds known, containing more than 17,000 distinct components (Hassanshahian and Cappello ; Head et al.). To simplify our approach, we investigated the biodegradation of two representatives of the main fractions of oil by two different bacterial model strains: Rhodococcus qingshengii TUHH-12, a degrader of the alkane n-hexadecane; and Sphingobium yanoikuyae B1, a bacterium capable of utilizing naphthalene, a polycyclic aromatic hydrocarbon (PAH) (Gibson et al. ). R. qingshengii and S. yanoikuyae, as well as other species of the genera Rhodococcus and Sphingobium have been isolated from deep-sea sediments (Colquhoun et al.[1998a]; Cui et al.; Heald et al. ; Peng et al.; Tapilatu et al. ; European Nucleotide Archive ; Wang and Gu ). Recently, Rhodococcus sp. and Sphingobium sp. were found to be present in sediment samples collected in May 2011, about 2 and 6 km away from the wellhead of the DWH (Liu and Liu ). In our experiments, both strains R. qingshengii TUHH-12 and S. yanoikuyae B1 were incubated at 0.1 MPa and at increasing pressures to determine the influence of pressure on the growth and hydrocarbon-degradation abilities of these strains.
Materials and methods
The alkane-degrading bacterium R. qingshengii TUHH-12 [DSM No.: 46766] was isolated from a seawater sample located directly beneath an ice cap swimming on the water during an expedition to the island of Spitzbergen, Norway, by Prof. Hauke Trinks (Hamburg University of Technology). The genome of this strain was recently sequenced (Lincoln SA, Penn State University, unpublished data).
S. yanoikuyae B1, purchased from DSMZ [DSM No.: 6900], was originally isolated from a polluted stream by Gibson et al. . This bacterium was preliminary identified as Beijerinckia species, but has later been reclassified as Sphingobium yanoikuyae B1 (Khan et al.). This strain is known to degrade different aromatic and polycyclic aromatic hydrocarbons (Gibson et al.; Lang ).
R. qingshengii TUHH-12 was cultivated on minimal-mineral medium with n-hexadecane as the sole carbon source. The medium consisted of 2.6 g Na2HPO4, 1.33 g KH2PO4, 1 g (NH4)2SO4 and 0.20 g MgSO4·7 H2O dissolved in 1000 mL of demineralized water. The medium was adjusted to pH 7. After sterilisation, 5 mL of trace element solution and 1 mL of vitamin solution were added. Both solutions were prepared as described in DSMZ methanogenium medium 141 and autoclaved or sterile filtered separately ([DSMZ 2012]). Cultures were incubated at room temperature and mixed at 200 rpm. The strain was kept on agar plates containing the same medium with 15 g/L agar added for solidification.
S. yanoikuyae B1 was cultured in Brunner mineral medium or on agar plates according to the DSMZ medium 457 (DSMZ [2012b]) at 30°C or at room temperature and 200 rpm. Naphthalene was used as sole carbon source.
Biodegradation experiments at high pressure
Ten high-pressure reactors consisting of stainless steel cylinders capped with bronze lids were used to simulate and to investigate biodegradation under elevated pressures as they occur in deep-sea environments. Additionally, ten aluminium reactors with the same geometry were used, serving as controls to monitor biodegradation under atmospheric pressure in simultaneous experiments (Figure 1). Both reactor types had a volume of 160 mL. For experiments with R. qingshengii TUHH-12, 20 mL mineral medium was filled into sterilized glass vials and supplemented with 1 mM n-hexadecane. For cultivation of S. yanoikuyae B1, 20 mL Brunner medium and 1.77 mM naphthalene were used. The amount of carbon in 1.77 mM naphthalene is equal to the amount of carbon in 1 mM n-hexadecane. The media were inoculated with a grown preculture of the respective bacterial strain, constituting 10% of the total volume. The vials were placed inside the reactors. The high-pressure reactors were pressurized with nitrogen gas up to 15 MPa (equivalent to 1,500 m DWH well depth). The cultures were incubated at room temperature. Since the oil components used in these experiments are nearly insoluble in water, stirring rates affect biodegradation rates; therefore, efficient mixing of the cultures was ensured by magnetic stirring at 200 rpm. Due to the immiscible two-phase system of oil and water and the impracticality of subsampling at high pressure, no representative samples could be taken from the reactors to monitor oil concentrations. Thus, for each point in time in a diagram the content of one reactor was processed. Before opening a reactor containing n-hexadecane, it was cooled for 5 h at 4 C to minimise evaporation of n-hexadecane. Bacterial growth was measured and the hydrocarbon concentrations were analysed to quantify the degree of biodegradation. In several repetitions of the experiments the effects of pressure were the same. Only slightly different growth and degradation rates were observed due to different sampling times and slightly differing inoculation cell numbers. Thus, the diagrams presented represent the typical course of growth and hydrocarbon degradation.
Determination of growth of S. yanoikuyae B1 with glucose at ambient and high pressure
In order to determine, whether the growth of S. yanoikuyae B1 was inhibited when growing on a non-toxic substrate at high pressure, we incubated the bacteria in Brunner medium with 1% glucose (w/v) at room temperature. After incubation for 44.5 hours at 0.1 MPa and at 15 MPa, the reactors were opened and cell numbers were determined.
Colony forming units (CFUs) of R. qingshengii TUHH-12 were determined by spreading 5 μL of the culture on Luria-Bertani (LB) agar plates in triplicate. The colonies were counted after 3 to 4 days of incubation at room temperature.
For S. yanoikuyae B1, plate counts were performed with R2A agar medium (DSMZ medium 830 (DSMZ [2012c])). The colonies were counted after 2 to 3 days of incubation at room temperature.
Quantification of the biodegradation of hydrocarbons by gas chromatography–mass spectrometry
After growth of the cultures, the remaining n-hexadecane or naphthalene was extracted from the complete culture medium of each reactor with 5 mL of n-hexane. Dodecane or n-hexadecane were added before extraction as internal standard respectively. An aliquot of 1 μL of the apolar phase, containing the hydrocarbon, was injected with a split ratio of 28:1 into a Hewlett-Packard 5890 Series II gas chromatograph (GC) coupled to a Hewlett-Packard 5971A mass selective detector. The GC was equipped with an Agilent HP-5MS column (30 m length, 0.25 mm internal diameter) and helium was used as carrier gas. The injector temperature for both n-hexadecane and naphthalene was increased from 80 C to 200 C at a rate of 0.5 C/s. The oven temperature program was as follows: an initial temperature of 80 C was increased to a final temperature of 200 C at a rate of 15 C/min, with a final 1 min hold at 200 C. The mass spectrometer was operated in full scan mode over 50 650 amu. The MS transfer line temperature was held at 320 C and the ion source temperature at 180 C.
Detection of hydroxylated intermediates in naphthalene conversion
For detection of hydroxylated intermediates in naphthalene conversion, the colourimetric method described by Arnow () was used. After 3 min centrifugation of 1 mL of a grown culture at 13,000 rpm, 200 μL of the supernatant were supplemented by 200 μL of the following reagents, in the order given, mixing well after each addition: 0.5 N HCl, nitrite-molybdate reagent, 1 N NaOH. If catechol or 1,2-dihydroxynaphthalene were present, a yellow colour resulted after addition of HCl and nitrite-molybdate reagent, and a red colour appeared after addition of NaOH. In the case of monohydroxylated compounds like salicylate or monohydroxynaphthalene the solution remained yellow.
Degradation of n-hexadecane by R. qingshengii TUHH-12 at ambient and high pressure
R. qingshengii TUHH-12 was cultivated on n-hexadecane as the sole source of carbon and energy. R. qingshengii TUHH-12 was found to grow well and to mineralize this hydrocarbon at atmospheric pressure (0.1 MPa) as well as at high pressure (15 MPa). At 15 MPa the degradation and growth behaviour was slightly different from that at atmospheric pressure (Figure 2). In both cases, a lag phase of 16 to 17 h was followed by an exponential growth phase and a stationary phase starting after 43 to 44 h of incubation. However, the growth rate of R. qingshengii TUHH-12 in the exponential phase was 0.36 h–1 at ambient pressure, from 17 h to 43 h, compared to 0.16 h–1 at high pressure, from 16 h to 44 h. In the stationary phase a higher cell density was reached at 0.1 MPa than at 15 MPa. The rate of degradation of n-hexadecane was 0.035 mM/h at ambient pressure from 17 to 43 h, and 0.019 mM/h at high pressure, from 16 to 44 h. In control experiments without bacteria at 15 MPa the n-hexadecane also slowly decreased although with a much slower rate of 0.007 mM/h.
Degradation of naphthalene by S. yanoikuyae B1 at ambient and high pressure
S. yanoikuyae B1 was incubated on naphthalene at high pressure (13.9 MPa) and at atmospheric pressure. The growth of S. yanoikuyae B1 on this PAH was strongly inhibited by high pressure. Bacteria grew at 0.1 MPa with a lag phase of 15 h, an exponential phase with a growth rate of 0.33 h−1 (from 15 to 28 h) and reached stationary phase at 28 h of incubation (Figure 3). At 13.9 MPa, however, CFUs of S. yanoikuyae B1 decreased after 15 h cultivation time until no CFUs could be counted after 66 h.
In 0.1 MPa experiments, the analysis of remaining naphthalene in the medium showed that the substrate was degraded completely after 19 h. The degradation rate of naphthalene, from 7 h to 19 h, was 0.064 mM/h. Because the bacteria did not grow at 13.9 MPa, we expected that at this pressure no naphthalene would be degraded at all. However, we also observed a decrease in substrate concentration at this pressure. With a conversion rate of 0.054 mM/h (from 7 h to 25 h), 96.6% of the naphthalene was converted after 75 h of incubation. After 66 h of incubation at elevated pressure, the initially colourless culture medium turned brown, while at ambient pressure the culture showed no change of colour.
In control experiments without bacteria about 20.8% of the initial naphthalene was found to be lost after 19 days of incubation at 14.2 MPa by evaporation of the highly volatile naphthalene. With a loss of about 25.3% at 0.1 MPa there was no significant difference to the incubation at high pressure.
Since S. yanoikuyae B1 did not grow at 13.9 MPa, we conducted additional experiments to determine the maximum pressure at which growth was possible. S. yanoikuyae B1 was incubated for 70 h on naphthalene at different pressures in the range between 0.1 MPa and 13 MPa (Figure 4). In the range of 0.1 to 8.8 MPa, the CFU counts remained relatively constant, but decreased when 8.8 MPa was exceeded. In incubations at and above 12 MPa no growth occurred after 70 h cultivation time and viable cell counts were lower than at the start of the incubation.
The naphthalene concentration decreased to below the limit of detection under both ambient pressure and pressures up to 12 MPa. At 12.5 MPa and 13 MPa, 25.2% and 17.9% of the original naphthalene remained, respectively, although CFUs did not increase. While at 0.1 MPa no change of colour could be observed, at 12.5 MPa, after 70 h of incubation, the medium had turned brown. In the test with the colour reagent of Arnow (), we found no colour, indicating that neither mono- nor dihydroxylated compounds like 1,2-dihydroxynaphthalene, catechol or salicylate were formed. We therefore assume that the formation of the brown colour was due to the polymerization of either quinones or aromatic ring cleavage products.
Growth of S. yanoikuyae B1 with glucose at different pressures
While S. yanoikuyae grew well on glucose at 0.1 MPa, at 15 MPa no growth at all was observed. After 44.5 hours the cell number had decreased from 5.98·105 to 1.7·105 cells per mL at 15 MPa. These results indicate that at high pressure it is not the conversion of naphthalene or its metabolites but rather another central function in S. yanoikuyae B1, which is inhibited.
Degradation of n-hexadecane by R. qingshengii TUHH-12 at ambient and high pressure
R. qingshengii TUHH-12 degraded the alkanes n-hexadecane, decane and tetracosane. R. qingshengii has been found to assimilate and mineralize different hydrocarbons including benzene, toluene, xylenes, naphthalene, n-dodecane (Benedek et al. ). However, until now, nothing was known about degradation capabilities of R. qingshengii at other than atmospheric pressure. Our experiments showed that the growth rate of R. qingshengii TUHH-12 at ambient pressure (0.36 h−1) was slightly higher than at 15 MPa (0.16 h−1). This leads to the conclusion that a pressure of 15 MPa has a slightly negative effect on the growth of this bacterium, suggesting it can be classified as a piezotolerant organism. These findings are confirmed by the work of Colquhoun et al. ([1998b]) and Heald et al. (), who showed that certain Rhodococcus strains were able to grow at even higher pressures of 40 MPa and 60 MPa on glucose yeast extract medium.
Effects of elevated pressure on the naphthalene degradation by S. yanoikuyae B1
The model strain S. yanoikuyae B1, used for PAH degradation in our high-pressure experiments, is capable of utilising a variety of aromatic compounds including biphenyl, anthracene, phenanthrene and naphthalene (Gibson et al. ), as well as toluene, cyclohexane and 1,3,5-trimethylbenzene (Lang ) as carbon sources for growth. We found significant differences in growth of S. yanoikuyae B1 with naphthalene at different pressures. These effects occurred at pressures lower than those typically assumed to be the threshold for pressure effects. First significant effects of high pressure on cellular components and processes of bacteria were found to start at 20 MPa, affecting the RNA transcription (Yayanos and Pollard ). Modifications of membrane fluidity were shown to occur at pressures above 100 MPa (Hauben et al.) and protein denaturation was observed at more than 400 MPa (Aertsen et al.).
In our experiments at 0.1 MPa S. yanoikuyae B1 was able to grow with naphthalene, whereas at 13.5 MPa bacteria did not grow at all and after 66 h of incubation, cells were no longer viable. A similar behaviour was found with glucose as carbon source. Thus, we conclude that S. yanoikuyae B1 is a piezosensitive strain that grew best and utilized naphthalene at an optimal rate at ambient pressure. Nevertheless, S. yanoikuyae B1 still metabolized naphthalene at 13.9 MPa, although slower than at 0.1 MPa, so that after 75 h of incubation 96.6% of the substrate was converted. We need to emphasize that the naphthalene-degradation capability of S. yanoikuyae B1 is much less sensitive to high pressure than growth is. This indicates a new type of piezosensitivity, which, to our knowledge, was not described in literature before.
We can only speculate about the reasons for the observed changes in growth and degradation ability of S. yanoikuyae B1 at high pressure. Even a combination of several pressure-induced effects is possible. The investigation of the specific reasons for the strong inhibition of growth and rather slight inhibition of naphthalene conversion of S. yanoikuyae B1 by high pressure emerges from our study as a new research topic.
So far in predicting the behavior and degradation of oil spills in deep-sea environments all models use data obtained at ambient pressure for calculating degradation rates. The results presented here show, that the effect of pressure cannot be neglected. When our data obtained under high pressure were included in a model describing the fate of the oil in the case of the Deepwater Horizon, the model predicted the observed changes in oil concentrations much better (Lindo-Atichati et al.).
Our experiments show that pressure affects both bacterial growth and hydrocarbon-degrading activity at pressures much lower than previously reported in the literature as they occur at modern deep-sea drilling sites. Consequently, pressure effects need to be considered as a crucial factor in predictions of oil biodegradation in deep waters.
Abe F, Horikoshi K: The biotechnological potential of piezophiles. Trends Biotechnol 2001, 19: 102–108. 10.1016/S0167-7799(00)01539-0
Aertsen A, Meersman F, Hendrickx MEG, Vogel RF, Michiels CW: Biotechnology under high pressure: applications and implications. Trends Biotechnol 2009, 27: 434–441. 10.1016/j.tibtech.2009.04.001
Arnow LE: Colorimetric determination of the components of 3,4-dihydroxyphenylalaninetyrosine mixtures. J Biol Chem 1937, 118: 531–537.
Atlas RM, Hazen TC: Oil biodegradation and bioremediation: a tale of the two worst spills in U.S. history. Environ Sci Technol 2011, 45: 6709–6715. 10.1021/es2013227
Bælum J, Borglin S, Chakraborty R, Fortney JL, Lamendella R, Mason OU, Auer M, Zemla M, Bill M, Conrad ME, Malfatti SA, Tringe SG, Holman H-Y, Hazen TC, Jansson JK: Deep-sea bacteria enriched by oil and dispersant from the Deepwater Horizon spill. Environ Microbiol 2012, 14: 2405–2416. 10.1111/j.1462-2920.2012.02780.x
Benedek T, Vajna B, Táncsics A, Márialigeti K, Lányi S, Máthé I: Remarkable impact of PAHs and TPHs on the richness and diversity of bacterial species in surface soils exposed to long-term hydrocarbon pollution. World J Microbiol Biotechnol 2013, 29: 1989–2002. 10.1007/s11274-013-1362-9
Colquhoun JA, Mexson J, Goodfellow M, Ward AC, Horikoshi K, Bull AT: Novel rhodococci and other mycolate actinomycetes from the deep sea. Antonie Van Leeuwenhoek 1998, 74: 27–40. 10.1023/A:1001743625912
Colquhoun JA, Heald SC, Li L, Tamaoka J, Kato C, Horikoshi K, Bull AT: Taxonomy and biotransformation activities of some deep-sea actinomycetes. Extremophiles 1998, 2: 269–277. 10.1007/s007920050069
Colwell RR, Walker JD, Cooney JJ: Ecological aspects of microbial degradation of petroleum in the marine environment. Crit Rev Microbiol 1977, 5: 423–445. 10.3109/10408417709102813
Cui Z, Lai Q, Dong C, Shao Z: Biodiversity of polycyclic aromatic hydrocarbon-degrading bacteria from deep sea sediments of the Middle Atlantic Ridge. Environ Microbiol 2008, 10: 2138–2149. 10.1111/j.1462-2920.2008.01637.x
DSMZ GmbH (2012a) 141 METHANOGENIUM MEDIUM., http://www.dsmz.de/microorganisms/medium/pdf/DSMZ_Medium141.pdf. Accessed 12 May 2014.
DSMZ GmbH (2012b) 457 MINERAL MEDIUM (BRUNNER)., http://www.dsmz.de/microorganisms/medium/pdf/DSMZ_Medium457.pdf. Accessed 12 May 2014.
DSMZ GmbH (2012c) 830 R2A MEDIUM., http://www.dsmz.de/microorganisms/medium/pdf/DSMZ_Medium830.pdf. Accessed 12 May 2014.
European Nucleotide Archive (2014) The EMBL. European Bioinformatics Institute, Hinxton, Cambridge, http://www.ebi.ac.uk/ena/data/view/KC894023. Accessed 29. May 2014
Gardner JV, Armstrong AA: The Mariana Trench: A new view based on multibeam echosounding. 2011.
Gibson DT, Roberts RL, Wells MC, Kobal VM: Oxidation of biphenyl by a Beijerinckia species. Biochem Biophys Res Co 1973, 50: 211–219. 10.1016/0006-291X(73)90828-0
Grossi V, Yakimov MM, Al Ali B, Tapilatu Y, Cuny P, Goutx M, La Cono V, Giuliano L, Tamburini C: Hydrostatic pressure affects membrane and storage lipid compositions of the piezotolerant hydrocarbon-degrading Marinobacter hydrocarbonoclasticus strain #5. Environ Microbiol 2010, 12: 2020–2033. 10.1111/j.1462-2920.2010.02213.x
Hassanshahian M, Cappello S: Crude Oil Biodegradation in the Marine Environments. In Chamy R. Edited by: Rosenkranz F. Biodegradation - Engineering and Technology, InTech; 2013:101–135.
Hauben KJ, Bartlett DH, Soontjens CC, Cornelis K, Wuytack EY, Michiels CW: Escherichia coli mutants resistant to inactivation by high hydrostatic pressure. Appl Environ Microbiol 1997, 63: 945–950.
Hazen TC, Dubinsky EA, DeSantis TZ, Andersen GL, Piceno YM, Singh N, Jansson JK, Probst A, Borglin SE, Fortney JL, Stringfellow WT, Bill M, Conrad ME, Tom LM, Chavarria KL, Alusi TR, Lamendella R, Joyner DC, Spier C, Baelum J, Auer M, Zemla ML, Chakraborty R, Sonnenthal EL, D’haeseleer P, Holman H-YN, Osman S, Lu Z, Nostrand JDV, Deng Y, et al.: Deep-sea oil plume enriches indigenous oil-degrading bacteria. Science 2010, 330: 204–208. 10.1126/science.1195979
Head IM, Jones DM, Röling WFM: Marine microorganisms make a meal of oil. Nat Rev Micro 2006, 4: 173–182. 10.1038/nrmicro1348
Heald SC, Brandão PFB, Hardicre R, Bull AT: Physiology, biochemistry and taxonomy of deep-sea nitrile metabolising Rhodococcus strains. Antonie Van Leeuwenhoek 2001, 80: 169–183. 10.1023/A:1012227302373
Jannasch HW, Taylor CD: Deep-sea microbiology. Annu Rev Microbiol 1984, 38: 487–514. 10.1146/annurev.mi.38.100184.002415
Kessler JD, Valentine DL, Redmond MC, Du M, Chan EW, Mendes SD, Quiroz EW, Villanueva CJ, Shusta SS, Werra LM, Yvon-Lewis SA, Weber TC: A persistent oxygen anomaly reveals the fate of spilled methane in the Deep Gulf of Mexico. Science 2011, 331: 312–315. 10.1126/science.1199697
Khan AA, Wang R-F, Cao W-W, Franklin W, Cerniglia CE: Reclassification of a polycyclic aromatic hydrocarbon-metabolizing bacterium, beijerinckia sp. strain B1, as sphingomonas yanoikuyae by fatty acid analysis, protein pattern analysis, DNA-DNA hybridization, and 16S ribosomal DNA sequencing. Int J Syst Bacteriol 1996, 46: 466–469. 10.1099/00207713-46-2-466
Lang E: Diversity of bacterial capabilities in utilizing alkylated benzenes and other aromatic compounds. Lett Appl Microbiol 1996, 23: 257–260. 10.1111/j.1472-765X.1996.tb00078.x
Leahy JG, Colwell RR: Microbial degradation of hydrocarbons in the environment. Microbiol Rev 1990, 54: 305–315.
Lindo-Atichati D, Paris CB, Le Hénaff M, Schedler M, Valladares Juárez AG, Müller R (2014) Simulating the effects of droplet size, high-pressure biodegradation, and variable flow rate on the subsea evolution of deep plumes from the Macondo blowout. Deep Sea Res Part II: Topical Stud Oceanogr, 10.1016/j.dsr2.2014.01.011 (in press)
Liu Z, Liu J: Evaluating bacterial community structures in oil collected from the sea surface and sediment in the northern Gulf of Mexico after the Deepwater Horizon oil spill. Microbiol Open 2013, 2: 492–504. 10.1002/mbo3.89
National Research Council (2003) Oil in the Sea III: Inputs, Fates, and Effects. The National Academies Press, Washington, DC
Peng F, Wang Y, Sun F, Liu Z, Lai Q, Shao Z: A novel lipopeptide produced by a Pacific Ocean deep-sea bacterium, Rhodococcus sp. TW53. J Appl Microbiol 2008, 105: 698–705. 10.1111/j.1365-2672.2008.03816.x
Powell SM, Bowman JP, Snape I: Degradation of nonane by bacteria from Antarctic marine sediment. Polar Biol 2004, 27: 573–578. 10.1007/s00300-004-0639-8
Redmond MC, Valentine DL: Natural gas and temperature structured a microbial community response to the Deepwater Horizon oil spill. Proc Natl Acad Sci U S A 2012, 109: 20292–20297. 10.1073/pnas.1108756108
Schwarz JR, Walker JD, Colwell RR: Deep-sea bacteria: growth and utilization of hydrocarbons at ambient and in situ pressure. Appl Microbiol 1974, 28: 982–986.
Schwarz JR, Walker JD, Colwell RR: Deep-sea bacteria: growth and utilization of n -hexadecane at in situ temperature and pressure. Can J Microbiol 1975, 21: 682–687. 10.1139/m75-098
Shiller AM, Joung D: Nutrient depletion as a proxy for microbial growth in Deepwater Horizon subsurface oil/gas plumes. Environ Res Lett 2012, 7: 045301. 10.1088/1748-9326/7/4/045301
Tapilatu Y, Acquaviva M, Guigue C, Miralles G, Bertrand J-C, Cuny P: Isolation of alkane-degrading bacteria from deep-sea Mediterranean sediments. Lett Appl Microbiol 2010, 50: 234–236. 10.1111/j.1472-765X.2009.02766.x
Valentine DL, Kessler JD, Redmond MC, Mendes SD, Heintz MB, Farwell C, Hu L, Kinnaman FS, Yvon-Lewis S, Du M, Chan EW, Tigreros FG, Villanueva CJ: Propane respiration jump-starts microbial response to a deep oil spill. Science 2010, 330: 208–211. 10.1126/science.1196830
Valentine DL, Mezić I, Maćešić S, Črnjarić-Žic N, Ivić S, Hogan PJ, Fonoberov VA, Loire S: Dynamic autoinoculation and the microbial ecology of a deep water hydrocarbon irruption. Proc Natl Acad Sci U S A 2012, 109: 20286–20291. 10.1073/pnas.1108820109
Wang YP, Gu J-D: Degradability of dimethyl terephthalate by Variovorax paradoxus T4 and Sphingomonas yanoikuyae DOS01 isolated from deep-ocean sediments. Ecotoxicology 2006, 15: 549–557. 10.1007/s10646-006-0093-1
Wang B, Lai Q, Cui Z, Tan T, Shao Z: A pyrene-degrading consortium from deep-sea sediment of the West Pacific and its key member Cycloclasticus sp. P1. Environ Microbiol 2008, 10: 1948–1963. 10.1111/j.1462-2920.2008.01611.x
Yakimov MM, Timmis KN, Golyshin PN: Obligate oil-degrading marine bacteria. Curr Opin Biotechnol 2007, 18: 257–266. 10.1016/j.copbio.2007.04.006
Yayanos AA, Pollard EC: A study of the effects of hydrostatic pressure on macromolecular synthesis in escherichia coli . Biophys J 1969, 9: 1464–1482. 10.1016/S0006-3495(69)86466-0
This research was made possible by a grant from British Petroleum (BP)/ The Gulf of Mexico Research Initiative. This publication was supported by the German Research Foundation (DFG) and the Hamburg University of Technology (TUHH) in the funding programme “Open Access Publishing”. The authors thank the company Technik Service Andreas Meyer for providing the high-pressure reactors and for technical advice. We are grateful to Eva Mong Su for her support in the lab and we thank Sara Lincoln from Penn State University for critical reading of the manuscript.
The authors declare that they have no competing interests.
MS participated in the design and performance of the experiments and drafted the manuscript. RH carried out the experiments and analysed the data. AGVJ participated in the design and coordination of the experiment, isolated the strain R. qingshengii TUHH-12, and contributed in the drafting of the manuscript. GG participated in the experimental design and contributed in the drafting of the manuscript. RM conceived of the study, participated in its design and contributed in the drafting of the manuscript. All authors read and approved the final manuscript.
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Schedler, M., Hiessl, R., Valladares Juárez, A.G. et al. Effect of high pressure on hydrocarbon-degrading bacteria. AMB Expr 4, 77 (2014). https://doi.org/10.1186/s13568-014-0077-0
- High pressure