Biomedical subjects

M Fingas

Publications and source records attributed to M Fingas.

8 recordsLinked to original sources

PubMed2001

Long-term fate and persistence of the spilled metula oil in a marine salt marsh environment degradation of petroleum biomarkers.

Three coastal sites, heavily oiled from the 1974 Metula oil spill in the Strait of Magellan [two are salt marshes (East and West) and the third, an intertidal asphalt pavement], were examined during May 1998. Complete 'total oil analyses' were performed on the oil samples collected from these sites. Chemical fingerprinting data reveal, except for those samples from the East Marsh untreated plots which were only lightly to moderately weathered, that the spilled oil has undergone significant alteration in chemical composition after 24 years. There are no fundamental differences between the heavily weathered West Marsh and treated East Marsh samples. However, the effect of experimental filling action conducted in 1993 has been to substantially promote plant recolonization. The asphalt pavement samples indicate extremely high degradation of oil hydrocarbons, evidenced by a complete loss of n-alkanes from n-C8 to n-C41 and by depletion of greater than 98% of the alkylated polycyclic aromatic hydrocarbon homologues. Even the most refractory biomarker compounds showed some degree of biodegradation. The biomarkers were generally degraded in the declining order of importance as follows: diasteranes>C27 steranes>tricyclic terpanes>pentacyclic terpanes>norhapanes approximately C29-alphabetabeta-steranes.

Oils↗

PubMed2001

An evaluation of field total petroleum hydrocarbon (TPH) systems.

An evaluation of several field kits and petroleum hydrocarbon measuring systems was conducted. The field kits were the immunoassay based EnviroGard petroleum fuels in soil test kit (EnviroGard, Millipore Canada, Mississauga, Ont., Canada), the turbidimetric based PetroFlag hydrocarbon test kit for soil (Dexsil, Hamden, CT, USA), a DR/2000 field kit (Hach Company, Loveland CO, USA) employing colorimetric test procedures and a total organic carbon (TOC) analysis instrument (Dohrmann Division, Rosemount Analytical Inc., Santa Clara, CA, USA) using oxidation principles. These procedures were compared to the traditional technique of extraction of the petroleum hydrocarbons using trichlorotrifluoroethane (Freon 113) as the solvent and subsequent infrared (IR) analysis using a portable fixed wavelength analyzer (Buck Scientific, East Norwalk, CT, USA). The EnviroGard kit was affected by the sample matrix. The soil type and the presence or lack thereof specific chemical components affected the capability to detect the petroleum hydrocarbon concentration. The PetroFlag soil test kit tended to generate results higher than the accepted concentration. The IR method was better capable of producing results similar to the expected concentration values of the prepared samples. Results indicate that the total organic carbon analysis technique evaluated is best suited for samples containing dissolved hydrocarbons in water and is not a preferred procedure for water samples containing dispersed or floating oil. At low concentrations of 10ppm and less, the TOC method and IR method have concentration values within a few parts-per-million (ppm) of each other, however, an examination of the trends in the results for all samples shows no similarity. This would indicate that the traditional extraction and infrared method and the total organic carbon method are not measuring the same parameter.Finally, the colorimetric field kit was capable of quantifying the concentration of oil in water samples within limits. The results from the oil-in-water method built into the unit at the factory were not comparable with analysis carried out by the infrared technique. With specific methods for each oil incorporated into the spectrophotometer, the comparability of data increased significantly. Results generated by the kit are dependent upon the color and amount of the oil in the sample. The kit is best suited for dark colored oils and the water samples with concentrations in the range of 10 to 85ppm by weight.

Colorimetry↗

PubMed2001

Solvent vapour monitoring in work space by solid phase micro extraction.

Solid phase micro extraction (SPME) is a fast, solvent-less alternative to conventional charcoal tube sampling/carbon disulfide extraction for volatile organic compounds (VOC). In this work, SPME was compared to the active sampling technique in a typical lab atmosphere. Two different types of fibre coatings were evaluated for solvent vapour at ambient concentration. A general purpose 100 microm film polydimethylsiloxane (PDMS) fibre was found to be unsuitable for VOC work, despite the thick coating. The mixed-phase carboxen/PDMS fibre was found to be suitable. Sensitivity of the SPME was far greater than charcoal sorbent tube method. Calibration studies using typical solvent such as dichloromethane (DCM), benzene (B) and toluene (T) showed an optimal exposure time of 5 min, with a repeatability of less than 20% for a broad spectrum of organic vapour. Minimum detectable amount for DCM is in the range of 0.01 microg/l (0.003 ppmv). Variation among different fibres was generally within 30% at a vapour concentration of 1 microg DCM/l, which was more than adequate for field monitoring purpose. Adsorption characteristics and calibration procedures were studied. An actual application of SPME was carried out to measure background level of solvent vapour at a bench where DCM was used extensively. Agreement between the SPME and the charcoal sampling method was generally within a factor of two. No DCM concentration was found to be above the regulatory limit of 50 ppmv.

Adsorption↗

PubMed2001

On site PCB analysis in support of a transformer rebuilding project.

In December 1997, Emergencies Science Division (ESD) was contracted by Natural Resources Canada (NRCAN) to perform on-site analyses in support of a transformer-rebuilding project at Sault Ste-Marie, Ont. Using a gas chromatograph with electron capture detector (GC/ECD) mounted in a mobile laboratory, PCB analyses were conducted on the original transformer oil, surface wipes, Varsol rinsing of the transformer tank interior and cooling fins. To assess the efficiency and validity of the decontamination process, PCB contamination was monitored closely on the rinse solvent. Surface wipe samples after wash down showed surface concentration of several hundred microg Aroclor 1254/100 cm(2), well below the acceptable limit of 8000 microg/100 cm(2). Because of the relatively large percentage of the internal surface area, the fin banks had to be rinsed exhaustively to meet the decontamination criteria. Final rinses of each of the seven fin banks of transformer 1 still showed presence of PCB, ranging from 80 to 590 ppm (microg/ml) with a mean value of 280 ppm. Upon completion of rebuilding, analysis of the R-Temp retro fill fluid showed 5 ppm at the initial power-up, increasing slightly to 16 ppm after 1 year of operation, which was far below the regulatory limit 50 ppm. The second transformer, by comparison, had a lower mean concentration of 54 ppm in the final fin rinse during decontamination. However, the backfill R-Temp showed an initial concentration of 38 ppm and remained essentially unchanged at 32 ppm after approximately 10 months of operation. Extensive comparison of GC and the quick test Clor-N-Oil kit were also carried out and showed generally good agreement. The use of an on-site GC was crucial in providing rapid and accurate analysis on-site, thus, enabling quick modifications to the decontamination strategies in order to meet the target PCB level. For projects of this nature, a GC/ECD was far superior to quick test kits by providing the selectivity and sensitivity for the diverse nature of the sample media.

Chromatography, Gas↗

PubMed2001

Preface.

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Environmental Monitoring↗

PubMed2001

Characterization and identification of a "mystery" oil spill from Quebec (1999).

This paper describes a case study in which advanced chemical fingerprinting and data interpretation techniques were used to characterize the chemical compositions and determine the source of an unknown spilled oil from Quebec. On 28 February 1999, significant amounts of oil was reported on the river banks of St. Laurence River in front of a company named "Thermex" (in a town - Beauharnois, Quebec, about 50 km northwest of Montreal). The spilled oil was suspected to be released from a nearby factory. In response to this specific site investigation needs, a tiered analytical approach using GC-MS and GC-flame ionization detection was applied. A variety of diagnostic ratios of "source-specific marker" compounds, in particular isomers of biomarkers and alkylated series of polycyclic aromatic hydrocarbons within the same alkylation groups, were determined and analyzed. The hydrocarbon analysis results reveal the following: (1) the spilled oil is very "specific", and is significantly different from most crude oils in chemical composition; (2) the oil in samples come from the same source, however, the spill sample 2569 was identified to contain a small amount (approximately 10%) of diesel; (3) the spilled oil was relatively "fresh", its chemical composition has not undergone significant alteration yet; (4) the spilled oil showed unusually high concentration of the US Environmental Protection Agency priority polycyclic aromatic hydrocarbons (PAHs). The "Pyrogenic Index" values were determined to be as high as 0.11-0.13, significantly higher than crude oils (<0.010) and heavy Bunker type fuels (0.015-0.060). This indicates significant contribution of PAH composition from pyrogenic components; (5) biomarkers were also detected, but their concentrations were unusually low in comparison to most crude oils.

Chromatography, Gas↗

PubMed1998

Headspace solid-phase microextraction for the determination of volatile and semi-volatile pollutants in water and air.

In this work we report the use of solid-phase microextraction (SPME) to extract and concentrate water-soluble volatile as well as semi-volatile pollutants. Both methods of exposing the SPME fibre were utilised: immersion in the aqueous solution (SPME) and in the headspace over the solution (HSSPME). The proposed HSSPME procedure was compared to conventional static headspace (HS) analysis for artificially spiked water as well as real water samples, which had been, equilibrated with various oil and petroleum products. Both techniques gave similar results but HSSPME was much more sensitive and exhibited better precision. Detection limits were found to be in the sub-ng/ml level, with precision better than 5% R.S.D. in most cases. To evaluate the suitability of SPME for relatively high contamination level analysis, the proposed HSSPME method was applied to the screening of run-off water samples that had heavy oil suspended in them from a tire fire incident. HSSPME results were compared with liquid--liquid extraction. Library searches were conducted on the resulting GC-MS total ion chromatograms to determine the types of compounds found in such samples. Both techniques found similar composition in the water samples with the exception of alkylnaphthalenes that were detected only by HSSPME. A brief study was carried out to assess using SPME for air monitoring. By sampling and concentrating the volatile organic compounds in the coating of the SPME fibre without any other equipment, this new technique is useful as an alternative to active air monitoring by means of sampling pumps and sorbent tubes.

Air Pollutants↗

PubMed1998

Comparison of oil composition changes due to biodegradation and physical weathering in different oils.

The well-characterized Alberta Sweet Mixed Blend oil and several other oils which are commonly transported in Canada were physically weathered and then incubated with a defined microbial inoculum. The purpose was to produce quantitative data on oil components and component groups which are more susceptible or resistant to biodegradation, and to determine how oils rank in relation to each other in terms of biodegradation potential. The biodegraded oils were characterized by quantitative determination of changes in important hydrocarbon groups including the total petroleum hydrocarbons, total saturates and aromatics, and also by quantitation of more than 100 individual target aliphatic, aromatic and biomarker components. The study reveals a pattern of distinct oil composition changes due to biodegradation, which is significantly different from the pattern due to physical or short-term weathering. It is important to be able to distinguish between these two forms of loss, so that loss due to weathering is not interpreted as loss due to biodegradation in the laboratory or in the field. Based on these findings, the oil composition changes due to biodegradation can be readily differentiated from those due to physical weathering. To rank the tested oils with respect to biodegradability, losses in total petroleum hydrocarbons and aromatics were used to calculate biodegradation potential indices, employing equations proposed by Environment Canada and the US National Oceanic and Atmospheric Administration. The different methods produced very similar biodegradation trends, confirming that patterns of oil biodegradability do exist.

Bacteria↗