Comprehensive Microbial Analysis for Hydrocarbon Degradation

There are many ways petroleum hydrocarbons can enter the environment, from pipeline ruptures and transportation spills to leaking underground storage tanks at retail gas stations. Regardless of the source, petroleum products are complex mixtures of hundreds of aliphatic, aromatic, cyclic and heterocyclic compounds.  Even for common classes of contaminants like benzene, toluene, ethylbenzene, and xylenes (BTEX), biodegradation can proceed by a multitude of pathways under both aerobic and anaerobic conditions.

QuantArray®-Petro has been designed to cost-effectively address these challenges. QuantArray®-Petro provides simultaneous quantification of twenty-two functional genes and microbial groups responsible for aerobic and anaerobic biodegradation of BTEX, polycyclic aromatic hydrocarbons (PAHs), fuel oxygenates, and a variety of short and long chain alkanes.

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QUANTARRAY®-PETRO ADVANTAGES:

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ACCURATE

Direct analysis of sample DNA removes the need to grow the bacteria, thus eliminating biases associated with traditional approaches (e.g., plate counts and MPNs).

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QUANTITATIVE

Absolute quantification of the concentrations of specific microorganisms and functional genes encoding enzymes responsible for contaminant biodegradation gives site managers a direct line of evidence to evaluate remediation options and monitor remedy performance. Results reported as cells/mL, cells/g, etc.

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COST EFFECTIVE

In a single analysis, QuantArray®-Petro quantifies functional genes responsible for aerobic and anaerobic biodegradation of petroleum hydrocarbons. QuantArray®-Petro has the same accuracy as CENSUS® qPCR, but is more comprehensive and cost-effective.

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INFORMATIVE

Is that a low, medium or high concentration of contaminant degraders? With the MI Database, clients can retrieve percentile rankings of their QuantArray® results to answer that question based on the tens of thousands of samples MI has received from sites around the world.

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SENSITIVE

The Method Detection Limit (MDL) is 10 cells/sample and the Practical Quantification Limit (PQL) is 250 cells/sample.

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SPECIFIC

Target specific bacterial groups (e.g., Methylibium petroleiphilum PM1) and functional genes (e.g., phenol hydroxylase, benzene carboxylase) responsible for contaminant biodegradation.

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FLEXIBLE

Analysis can be performed on almost any type of sample (water, soil, sediments, Bio-Traps®, and others).

HOW TO USE QUANTARRAY®-PETRO:

Along with contaminant concentrations and geochemical parameters, the concentrations of specific microorganisms and functional genes responsible for contaminant biodegradation are a key component of remedy selection and performance monitoring at sites impacted by petroleum hydrocarbons.

Use QuantArray® to help answer…

  • How feasible is MNA? Is enhanced bioremediation needed?
    • What are the concentrations of contaminant degraders under existing conditions?
    • Are degrader concentrations greater in impacted wells than background wells?
    • Based on the MI Database, are concentrations of contaminant degraders low, medium, or high in the plume?

QuantArray-Petro Graphs

 

  • Is enhanced bioremediation effective?
    • Did concentrations of contaminant degraders and functional genes increase in response to treatment?
    • Are additional types of degraders and functional genes now detected that were previously below detection limits?

GENE TARGETS INCLUDED IN A SINGLE QUANTARRAY®-PETRO qPCR ANALYSIS

TARGETCODERELEVANCE / DATA INTERPRETATION
Toluene DioxygenaseTODToluene/benzene dioxygenase (TOD) incorporates both atoms of molecular oxygen directly into the aromatic ring. Although commonly called toluene dioxygenase, the substrate specificity of this enzyme is relaxed, allowing growth on toluene, benzene, and chlorobenzene along with co-oxidation of a variety of compounds including ethylbenzene, p-xylene, m-xylene, and TCE.
Phenol HydroxylasePHEIn general, phenol hydroxylases (PHE) catalyze the continued oxidation of phenols produced by RMOs. However, the difference between toluene monooxygenases (RMOs) and phenol hydroxylases (PHEs) is not absolute in terms of substrate specificity and catabolic function.
Ring Hydroxylating Toluene MonooxygenaseRDEGLike RMO, catalyzes the initial oxidation and sometimes second oxidation steps in aerobic BTEX biodegradation. The RDEG assay quantifies toluene-2-monooxygenases.
Ring Hydroxylating Toluene MonooxygenaseRMOCatalyzes the initial and sometimes second oxidation steps in aerobic BTEX biodegradation. The ring hydroxylating monooxygenases can be further described based upon where they attack the aromatic ring. The RMO assay targets as toluene-3-monooxygenases and toluene-4-monooxygenases.
Toluene/Xylene MonooxygenaseTOLThe final known pathway for aerobic toluene biodegradation involves an initial monooxygenase attack at the methyl group by a toluene/xylene monooxygenase.
Ethylbenzene DioxygenaseEDOSimilar to TOD, this group of aromatic oxygenases exhibits relatively broad specificity and are responsible for aerobic biodegradation of alkylbenzenes including ethylbenzene and isopropylbenzene or cumene.
Biphenyl/
Isopropylbenzene Dioxygenase
BPH4In environmental restoration, biphenyl dioxygenases are best known for cometabolism of polychlorinated biphenyls (PCBs). However, this subfamily includes benzene and isopropylbenzene dioxygenases from Rhodococcus spp.
Methylibium petroleiphilum PM1PM1Targets M. petroleiphilum PM1, one of the few organisms isolated to date which is capable of utilizing MTBE and TBA as growth supporting substrates.
TBA MonooxygenaseTBATargets the functional gene which catalyzes the continued biodegradation of TBA, an intermediate produced during aerobic MTBE biodegradation. TBA is also produced as a metabolite of aerobic biodegradation of ETBE by most known strains.
Naphthalene DioxygenaseNAHInitiates aerobic metabolism of naphthalene by incorporating both atoms of molecular oxygen into the ring. The broad substrate specificity of naphthalene dioxygenase has been widely noted. When expressed, naphthalene dioxygenase is capable of catalyzing the oxidation of larger PAHs like anthracene, phenanthrene, acenaphthylene, acenaphthene, and fluorine.
Naphthalene-Inducible DioxygenaseNidATargets the naphthalene inducible dioxygenases found in Mycobacterium and Rhodococcus spp. which are capable of mineralizing naphthalene and degrading some higher molecular weight PAHs including pyrene and benzo[a]pyrene.
Phenanthrene DioxygenasePHNThe PHN assays quantify phenanthrene/naphthalene dioxygenase genes from a diverse collection of microorganisms including Pseudomonas, Burkholderia, Sphingomonas, and Acidovorax spp. As with other naphthalene dioxygenases, substrate specificity is relatively broad.
Alkane MonooxygenaseALKInitiates the aerobic biodegradation of n-alkanes with carbon lengths from C5 to C16.
Alkane MonooxygenaseALMACatalyzes the aerobic biodegradation of C20-C32 alkanes by some Alcanivorax species considered dominant in marine systems.
Benzoyl Coenzyme A ReductaseBCRBenzyl-CoA is the central intermediate in the anaerobic biodegradation of many aromatic hydrocarbons. Benzoyl-CoA Reductase (BCR) is the essential enzyme for reducing the benzene ring structure.
Benzylsuccinate SynthaseBSSThe first step in anaerobic biodegradation of toluene, mediated by benzylsuccinate synthase (bssA), is the addition of fumarate onto the toluene methyl group to form benzylsuccinate. Some bacterial isolates utilize this same metabolic approach for anaerobic biodegradation of ethylbenzene and xylenes.
Anaerobic Benzene CarboxylaseABCAlthough additional pathways are possible, the only pathway for anaerobic biodegradation of benzene elucidated to date is initiated by a benzene carboxylase enzyme.
Naphthyl-2-methyl-succinate synthaseMNSSAGene encoding the enzyme responsible for initiating anaerobic biodegradation of 2-methylnaphthalene by catalyzing the addition of fumarate onto the methyl group. MNSSA is analogous to the well-studied benzylsuccinate synthase (BSS) described for anaerobic biodegradation of toluene.
Anaerobic Naphthalene CarboxylaseANCTo date, the only pathway that has been characterized for anaerobic biodegradation of naphthalene is initiated by a naphthalene carboxylase enzyme.
Alkylsuccinate SynthaseASSAInitiates anaerobic biodegradation of alkanes with chain lengths from C6 to at least C18.
Total EubacteriaEBACIndex of total bacterial biomass
Sulfate Reducing BacteriaAPSQuantification of sulfate reducing bacteria provides an additional line of evidence when evaluating redox conditions and terminal electron accepting processes.

FREQUENTLY ASKED QUESTIONS

How soon can I expect to receive the QuantArray®-Petro results?

The turnaround time to receive a QuantArray®-Petro report is 7-14 calendar days.

Can QuantArray®-Petro results be used to calculate degradation rates?

An estimated first-order rate constant for anaerobic toluene biodegradation can be calculated using toluene concentration and abundance of the benzylsuccinate synthase gene (bssA). The bssA gene target is included in the QuantArray®-Petro suite, and the rate constant calculator can be found here. Additional research is needed to link other gene targets to degradation rates.

Are there additional analyses to consider if LNAPL is present?

Natural source zone depletion (NSZD) is the process where light non-aqueous phase liquid (LNAPL) petroleum hydrocarbons are lost from the subsurface due to naturally occurring dissolution, volatilization, and biodegradation. To evaluate microbial communities involved in NSZD and assess the potential for biodegradation of LNAPL in the source zone, QuantArray®-NSZD testing is recommended.

How is QuantArray® different from CENSUS® qPCR and multiplex qPCR?

In many respects, QuantArray® is the same as conventional qPCR, so you can expect the same level of accuracy and precision.  Other methods like multiplex qPCR have been described that achieve some level of parallel quantification.  However, there is a fundamental difference between the QuantArray® and multiplex qPCR.  For multiplex qPCR, multiple primer sets are added to a reaction mixture to quantify multiple gene targets whereas QuantArray® employs discrete through-holes for individual qPCR reactions ensuring that reaction kinetics are not compromised. Download our “CENSUS® versus QuantArray®” white paper for further information.

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RESOURCES FOR PETROLEUM HYDROCARBON REMEDIATION

CASE STUDIES FROM HYDROCARBON-IMPACTED SITES

QuantArray®-Petro: Evaluating a Transition to MNA

For this project, site managers wanted to know if they could transition to MNA. By utilizing QuantArray®-Petro and SIP, we were able to provide them the analysis to support an MNA management decision.

QuantArray®-Petro: Assessment of Hydrocarbon Impact in Drinking Water Aquifer

• A homeowner dependent on a domestic water well suddenly saw an accumulation of a black precipitant clogging the pre-filter of their water treatment system. Two years previous to this observation there was a release of gas condensate hydrocarbons and saltwater upgradient of their property.

• The results of the QuantArray®-Petro analysis provided evidence of hydrocarbon impact in the drinking water aquifer upgradient of the homeowner’s property in a remarkably cost-effective manner and contributed to a settlement of this case to the benefit of the homeowner.

QuantArray®-Petro: Effectiveness of Oxygen Addition at a Former Gas Station

• Groundwater at a former gasoline service station was impacted by leaking underground storage tanks and associated piping. Although contaminant trends and geochemistry suggested that MNA could be an appropriate site management strategy, the need for more rapid site closure led to a decision to enhance biodegradation of BTEX and MTBE aerobically with injection of an oxygen releasing compound.

QuantArray®-Petro: MNA Assessment at a Crude Oil Impacted Site

At a crude oil impacted site, project managers were considering MNA as a site management strategy based on favorable contaminant concentration trends and geochemistry in groundwater. However, additional lines of evidence were required.

Together with contaminant concentration trends and geochemistry, the direct microbial data provided multiple lines of evidence to support a confident MNA decision resulting in significant cost savings over enhanced remediation.

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