Unresolved complex mixture, or hump, is a feature frequently observed in gas chromatographic data of crude oils and extracts from organisms exposed to oil. The reason for the UCM hump appearance is that GC cannot resolve and identify a significant part of the hydrocarbons in crude oils. The resolved components appear as peaks while the UCM appears as a large background/platform. In non-biodegraded oils the UCM may comprise less than 50% of the total area of the chromatogram, while in biodegraded oils this figure can rise to over 90%. UCMs are also observed in certain refined fractions such as lubricating oils and references therein. One reason why it is important to study the nature of UCMs is that some have been shown to contain toxic components, but only a small range of known petrogenic toxicants, such as the USEPA list of 16 polycyclic aromatic hydrocarbons, tend to be routinely monitored in the environment. Analysis of the hydrocarbon fraction of crude oils by gas chromatography reveals a complex mixture containing many thousands of individual components. Components that are resolved by GC have been extensively studied e.g. However, despite the application of many analytical techniques the remaining components have, until very recently, proved difficult to separate due to the large numbers of co-eluting compounds. Gas chromatograms of mature oils have prominent n-alkane peaks which distract attention from the underlying unresolved complex mixture of hydrocarbons often referred to as the ‘hump’. Processes such as weathering and biodegradation result in a relative enrichment of the UCM component by removal of resolved components and the creation of new compounds. It has been shown that both resolved and unresolved components of oils are subject to concurrent biodegradation, i.e. it is not a sequential process, but due to the recalcitrant nature of some components, the rates of biodegradation of individual compounds greatly varies. The UCM fraction often represents the major component of hydrocarbons within hydrocarbon-polluted sediments and biota e.g. A number of studies has now demonstrated that aqueous exposure to components within the UCM can affect the health of marine organisms, including possible hormonal disruption, and high concentrations of environmental UCMs have been strongly implicated with impaired health in wild populations.
Environmental UCMs result from highly degraded petroleum hydrocarbons and once formed they can stay largely unchanged in sediments for many years. For example, in 1969 a diesel oil spill contaminated saltmarsh sediment within Wild Harbor River, US; by 1973 only a baseline hump was observed, which remained largely unchanged within the anaerobic sediment for 30. In a study of the potential for UCM-dominated oil to be further degraded, it was concluded that even using bacteria specifically adapted for complex UCM hydrocarbons in conjunction with nutrient enrichment, biodegradation rates would still be relatively slow. Bacterial degradation of hydrocarbons is complex and will depend on environmental conditions.
Analysis of UCM hydrocarbons
A relatively recent analytical tool that has been used for the separation of UCMs is comprehensive two-dimensional GC . This powerful technique, introduced by Liu and Phillips combines two GC columns with different separation mechanisms: typically a primary column that separates compounds based on volatility coupled to a second short column that separates by polarity. The two columns are connected by a modulator, a device that traps, focuses and re-injects the peaks that elute from the first column into the second column. Each peak eluting from the first column is further separated on the second column. The second separation is rapid, allowing the introduction of subsequent fractions from the first column without mutual interference. Dallüge et al. reviewed the principles, advantages and main characteristics of this technique. One of the main advantages is the very high separation power, making the technique ideal for unravelling the composition of complex mixtures. Another important feature of GC×GC is that chemically related compounds show up as ordered structures within the chromatograms, i.e. isomers appear as distinct groups in the chromatogram as a result of their similar interaction with the second dimension column phase. The use of GC×GC for the characterization of complex petrochemical mixtures has been extensively reviewed. Most research into petrochemical hydrocarbons using GC×GC has utilised flame ionisation detection but mass spectrometry is necessary to obtain the structural information necessary to identify unknown compounds. Currently, only time-of-flight MS can deliver the high acquisition rates required to analyse GC×GC.
Toxicity of UCM hydrocarbon components
There is compelling evidence that components within some UCMs are toxic to marine organisms. The clearance rate of mussels was reduced by 40% following exposure to a monoaromatic UCM derived from a Norwegian crude oil. The toxicity of monoaromatic UCM components was further evidenced by an elegant set of experiments using transplantations of clean and polluted mussels. Recent analysis by GC×GC-ToF-MS of UCMs extracted from the mussel tissues, has shown that they contain a vast array of both known and unknown compounds. The comparative analysis of UCMs extracted from mussels known to possess high, moderate and low Scope for Growth, a measure of the capacity for growth and reproduction, revealed that branched alkylbenzenes represented the largest structural class within the UCM of mussels with low SfG; also, branched isomers of alkyltetralins, alkylindans and alkylindenes were prominent in the stressed mussels. Laboratory toxicity tests using both commercially available and specially synthesised compounds revealed that such branched alkylated structures were capable of producing the observed poor health of the mussels. The reversible effects observed in mussels following exposure to the UCM hydrocarbons identified to date are consistent with non-specific narcosis mode of action of toxicity. There is no evidence that toxic UCM components can biomagnify through the food chain. Crabs that were fed a diet of mussels contaminated with environmentally realistic concentrations of branched alkylbenzenes, suffered behavioural disruption but only a small concentration of the compounds were retained in the midgut of the crabs. Within marsh sediments still contaminated with high concentrations of UCM hydrocarbons from the Florida barge oil spill in 1969 the behaviour and feeding of fiddler crabs was reported to be affected.
Polar UCMs
Much of the past research into the composition and toxicity of UCM hydrocarbons has been conducted by the at the University of Plymouth, UK. As well as the hydrocarbon UCM, oils also contain more polar compounds such as those containing oxygen, sulphur or nitrogen. These compounds can be very soluble in water and hence bioavailable to marine and aquatic organisms. Polar UCMs are present within produced waters from oil rigs and from oil sands processing. A polar UCM fraction extracted from North Sea oilproduced water was reported to elicit hormonal disruption by way of both estrogen receptor agonist and androgen receptor agonist activity. Ongoing concern regarding the potential toxicity of components within Athabasca Oil Sands tailings ponds has highlighted the need for identification of the compounds present. Until recently, such positive identification of individual so-called naphthenic acids from oil sands produced waters had so far eluded characterisation but recent research by PEGG presented at a SETAC conference in 2010 revealed that, using a new GCxGC-TOF-MS, it was possible to resolve and identify a range of new compounds within such highly complex extracts. One group of compounds found to be present were tricyclic diamondoid acids. These structures had previously not even been considered as naphthenic acids and suggests an unprecedented degree of biodegradation of some of the oil in the oil sands.
