Variation in Petroleum Hydrocarbon Chain Lengths with Depth at a Former Crude Oil and Natural Gas ProductionFacility

An investigation was performed at a former crude oil and natural gas production facility to evaluate whether releases from the product flowlines, gathering lines or water injection lines had impacted soil beneath the site. Thirty-six trenches were initially excavated and sampled beneath the former piping runs to a maximum depth of 6?m. After the trenching investigation, nine soil boreholes were advanced and sampled to a depth of approximately 18?m to further delineate the lateral and vertical extent of impacted soil. Soil samples collected from the trenches and boreholes were analyzed for total petroleum hydrocarbons (TPH) in accordance with ASTM Method 2887. The results of the investigation indicated that TPH impacted soil was present within several areas of the 40-ha site. The petroleum hydrocarbons generally had chain lengths ranging from C₆ to C₃₅, characteristic of light crude oil. The impacted soil also contained condensate, the volatile portion of crude oil. Condensate consists of short-chain hydrocarbons (C₁ to C₁₂) and is characterized by low levels of aromatic volatile organic compounds (VOCs). The condensate typically was more prevalent at depths below 4.5?m than the less volatile, longer chain length hydrocarbons. Statistical analysis of TPH data collected during subsequent excavation activities showed that the mean percentage of condensate was significantly greater at depths below 4.5?m than in shallower samples. In contrast, the mean percentage of TPH compounds in the diesel range (C₁₄ to C₂₃) was significantly greater in samples collected at depths above 4.5?m. The difference in the mean percentage of heavier hydrocarbons (C₂₄ to C₄₄+) with depth was not statistically significant.     

Evaluation of the total petroleum hydrocarbon (TPH) standard for JP‐4 jet fuel

The potential for use of alternatives to total petroleum hydrocarbons (TPH) for remediation purposes was examined specifically for JP‐4 fuel. The study objective was to determine the scientific basis for use of fuel constituents other than TPH in establishing soil cleanup standards at JP‐4‐contaminated sites. The general bases for TPH soil cleanup standards or goals were characterized. Problems with the use of TPH for cleanup included its lack of specificity (e.g., method‐, medium‐, and time‐from‐spill‐dependency) as well as the lack of toxicological relevance. JP‐4 fuel constituents (alkanes, BTEX [i.e., benzene, toluene, ethylbenzene, xylenes], polycyclic aromatic hydrocarbons [PAHs, i.e., chrysene], and naphthalenes) were identified as potential TPH alternatives. A series of criteria were applied to assess the viability of the use of specific JP‐4 constituents as TPH alternatives, and to select the most appropriate alternative. Criteria included chemical fate and transport, toxicity, and regulatory standards for relevant media of concern. Consideration of these criteria ultimately resulted in selection of benzene as the JP‐4 indicator of choice. The potential for altering risk‐based benzene soil cleanup concentrations (preliminary remediation goals, PRGs) was examined, and encompassed the basis for the existing benzene cancer slope factor (SF) as well as the role of distributional analysis of exposure parameters (Monte Carlo) that might be employed at JP‐4 spill sites. Results and conclusions are presented, and the implications for fuels other than JP‐4 are also discussed.     

Attenuation of petroleum hydrocarbons by weathering: a case study

Possible alterations in the distribution and composition of total petroleum hydrocarbon (TPH), polycyclic aromatic hydrocarbons (PAHs), and benzene, toluene, ethyl benzene, and xylene isomers (BTEX) in the released oil at Idu-Ekpeye in Niger Delta (Nigeria) were studied within two seasonal variations of two months and six months, with a view to assessing the level of attenuation of these hydrocarbons in impacted soils. Although there were significant contaminations in the kerosene range (n-C10-n-C14) two months after, especially of the n-C12 and n-C13 fractions, the complete disappearance of the n-C8 to n-C23 hydrocarbons, including the acyclic isoprenoids (pristane and phytane), and the reduced amounts of PAHs, and BTEX, six months after, provided substantial evidence of attenuation as indicated in the reduction in total hydrocarbon content (THC) from 61.17 to 42.86%. Soil physicochemical properties such as pH, moisture content, heavy metal, TOC, and TOM, all provided corroborative evidence of hydrocarbon attenuation. The pristane/phytane ratio of the spill samples suggests that the spilled oil was genetically oxic.     

Cleanup standards for petroleum hydrocarbons. Part 1. Review of methods and recent developments

Many states across the U.S. use the total petroleum hydrocarbon (TPH) measurement as a regulatory tool for setting cleanup standards for underground storage tank sites and other petroleum‐related sites requiring cleanup. In Part I of this article, alternative techniques for developing site‐specific cleanup standards for petroleum hydrocarbons are reviewed, including the use of chemical fingerprinting, constituent analysis, and risk assessment methods that address hydrocarbons found in the environment. New developments in standard setting for petroleum hydrocarbons are described, including risk‐based standards for hydrocarbon mixtures and ecological risk‐based approaches. In Part 2 of this article, the cost‐effectiveness and accuracy of the most commonly used of these approaches will be evaluated by comparing a generic TPH cleanup standards approach with site‐specific cleanup standards approaches for two actual sites in Washington State, a neighborhood gas station and a former bulk fuel storage facility.     

Estimation of the migration potential of diesel fuel constituents from soil to ground water: A case study

A methodology for estimating the migration potential of diesel fuel constituents from soil to ground water was developed for a large commercial property impacted by diesel fuel. The diesel fuel impacts are associated with former railyard practices that occurred prior to 1970. The site is being redeveloped for commercial use. The proposed improvements for the site include an asphalt‐paved parking lot over the location of the diesel fuel‐impacted soils. The methodology is based on the composition of weathered diesel fuel and the migration characteristics and toxicity data of the diesel fuel constituents. Based on these considerations, the two elements of the methodology are (1) an evaluation of the migration potential of diesel fuel constituents in soil using the soil synthetic rainwater leachate laboratory analysis; and (2) a health‐risk assessment of the diesel fuel ground water impacts. This approach provided sufficient site‐specific data to support a regulatory agency decision allowing development to continue without active remediation of the site soils. If the methodology had not been applied to the site, a remedial method based on a 100 mg/kg to 1000 mg/kg TPH underground storage tank (UST) program soil cleanup level would have likely been required. Considering the project's time constraints and financial requirements, remedial options such as offsite disposal or onsite thermal treatment would have been used resulting in cleanup costs likely exceeding $500, 000. The potential value of this methodology can be best appreciated considering that, based on EPA estimates, there are approximately 295, 000 contaminated UST sites and a significant portion of these sites are contaminated with diesel fuel. These sites could benefit considerably from this approach.     

Comparison of Trees and Grasses for Rhizoremediation of Petroleum Hydrocarbons

Rhizoremediation of petroleum contaminants is a phytoremediation process that depends on interactions among plants, microbes, and soils. Trees and grasses are commonly used for phytoremediation, with trees typically being chosen for remediation of BTEX while grasses are more commonly used for remediation of PAHs and total petroleum hydrocarbons. The objective of this review was to compare the effectiveness of trees and grasses for rhizoremediation of hydrocarbons and address the advantages of each vegetation type. Grasses were more heavily represented in the literature and therefore demonstrated a wider range of effectiveness. However, the greater biomass and depth of tree roots may have greater potential for promoting environmental conditions that can improve rhizoremediation, such as increased metabolizable organic carbon, oxygen, and water. Overall, we found little difference between grasses and trees with respect to average reduction of hydrocarbons for studies that compared planted treatments with a control. Additional detailed investigations into plant attributes that most influence hydrocarbon degradation rates should provide data needed to determine the potential for rhizoremediation with trees or grasses for a given site and identify which plant characteristics are most important.     

Cleanup standards for petroleum hydrocarbons. part 2. Case study comparisons of site‐specific cleanup standards with generic TPH standards

Many states across the U.S. use the total petroleum hydrocarbon (TPH) measurement as a regulatory tool for setting cleanup standards for underground storage tank sites and other petroleum‐related sites requiring cleanup. In Part 1 of this article (Michelsen and Petito Boyce, J. Soil Contam., 2(2): 109–124), alternative techniques and new methods for developing site‐specific cleanup standards for petroleum hydrocarbons were reviewed, including the use of chemical fingerprinting, constituent analysis, and human health and ecological risk assessment methods. In Part 2 of this article, the cost effectiveness and accuracy of these approaches are evaluated by comparing a generic TPH cleanup standards approach with site‐specific cleanup standards approaches for two actual sites in Washington State, a neighborhood gas station and a former bulk fuel storage facility. Based on these case studies, as well as consideration of other available approaches discussed in Part 1 of this article, recommendations are provided for selecting the most appropriate method of developing cleanup standards at a petroleum‐contaminated site.     

Effects of low temperature and freeze-thaw cycles on hydrocarbon biodegradation in Arctic tundra soil.

Degradation of petroleum hydrocarbons was monitored in microcosms with diesel fuel-contaminated Arctic tundra soil incubated for 48 days at low temperatures (-5, 0, and 7 degrees C). An additional treatment was incubation for alternating 24-h periods at 7 and -5 degrees C. Hydrocarbons were biodegraded at or above 0 degrees C, and freeze-thaw cycles may have actually stimulated hydrocarbon biodegradation. Total petroleum hydrocarbon (TPH) removal over 48 days in the 7, 0, and 7 and -5 degrees C treatments, respectively, was 450, 300, and 600 microg/g of soil. No TPH removal was observed at -5 degrees C. Total carbon dioxide production suggested that TPH removal was due to biological mineralization. Bacterial metabolic activity, indicated by RNA/DNA ratios, was higher in the middle of the experiment (day 21) than at the start, in agreement with measured hydrocarbon removal and carbon dioxide production activities. The total numbers of culturable heterotrophs and of hydrocarbon degraders did not change significantly over the 48 days of incubation in any of the treatments. At the end of the experiment, bacterial community structure, evaluated by ribosomal intergenic spacer length analysis, was very similar in all of the treatments but the alternating 7 and -5 degrees C treatment.     

Transport model parameter sensitivity for soil cleanup level determinations using sesoil and at123d in the context of the california leaking underground fuel tank field manual

The California Leaking Underground Fuel Tank Field Manual (LUFT Manual; WRCB, 1989) is used by the regulatory community, consultants, and industry in California to determine acceptable cleanup concentration goals for the remediation of hydrocarbon‐affected soils. The LUFT methodology is a semiquanitative approach that uses rating tables that consider the effects of local precipitation and the depth to ground water from the deepest affected soils, as well as anthropogenic and geologic factors. The latter factors are evaluated subjectively, with only the effects of local precipitation and depth to ground water accounted for quantitatively. To assess the effects of these variables on the hydrocarbon concentrations that could be left in soil while protecting ground water quality, the state of California performed modeling using SESOIL and AT123D. The results from a small number of simulations covering a very narrow range of input parameter values were then extrapolated to form the LUFT Manual rating tables, which cover ranges in precipitation and depth to ground water of 0 to 40 in. per year and 5 to 150 ft, respectively. Although the use of these tables generally results in conservative cleanup level determinations, the extrapolation method used and the lack of consideration for extremely sensitive input parameters (other than precipitation and depth to ground water) in the development of the tables calls into question their validity. A sensitivity analysis on the model input parameters is presented that highlights several critical input parameters that greatly affect cleanup concentration determinations. The sensitivity analysis shows that certain parameters that were fixed at conservative levels for the development of the LUFT Manual rating tables (e.g., biodegradation rate and soil organic carbon content) are more sensitive than precipitation and the depth to ground water. In many cases, site‐specific analysis will thus yield higher soil cleanup concentrations that are still protective of water quality. In addition, in some instances the cleanup concentrations in the LUFT Manual tables are not protective of water quality. To provide a firm basis for soil cleanup‐level determinations, site‐specific analysis is recommended whenever significant quantities of soil may require remediation. This will provide more cost‐effective remediation and greater assurance of water quality protection.     

Biodegradation of aged diesel in diverse soil matrixes: impact of environmental conditions and bioavailability on microbial remediation capacity

While bioremediation of total petroleum hydrocarbons (TPH) is in general a robust technique, heterogeneity in terms of contaminant and environmental characteristics can impact the extent of biodegradation. The current study investigates the implications of different soil matrix types (anthropogenic fill layer, peat, clay, and sand) and bioavailability on bioremediation of an aged diesel contamination from a heterogeneous site. In addition to an uncontaminated sample for each soil type, samples representing two levels of contamination (high and low) were also used; initial TPH concentrations varied between 1.6 and 26.6 g TPH/kg and bioavailability between 36 and 100 %. While significant biodegradation occurred during 100 days of incubation under biostimulating conditions (64.4–100 % remediation efficiency), low bioavailability restricted full biodegradation, yielding a residual TPH concentration. Respiration levels, as well as the abundance of alkB, encoding mono-oxygenases pivotal for hydrocarbon metabolism, were positively correlated with TPH degradation, demonstrating their usefulness as a proxy for hydrocarbon biodegradation. However, absolute respiration and alkB presence were dependent on soil matrix type, indicating the sensitivity of results to initial environmental conditions. Through investigating biodegradation potential across a heterogeneous site, this research illuminates the interplay between soil matrix type, bioavailability, and bioremediation and the implications of these parameters for the effectiveness of an in situ treatment.     

Prepared Bed Land Treatment of Soils Containing Diesel and Crude Oil Hydrocarbons

An ex situ, field-scale, prepared bed land treatment unit (LTU) was used to bio-remediate soils containing petroleum hydrocarbons. Two soils were treated in side-by-side units to compare performance: (1) a clayey silt containing crude oil hydrocarbons from releases 30 to 40 years ago and (2) a silty sand containing diesel fuel hydrocarbons from a leak about three years prior to the bioremediation. The effectiveness of the bioremediation in the LTU was evaluated over a period of 18 months. The results indicated that: (1) prepared bed bioremediation reduced the hydrocarbon concentration, mobility, and relative toxicity in the soil with the diesel fuel, and (2) chemical bioavailability appeared to limit bioremediation of the soil containing the crude oil hydrocarbons. Although the soils containing the crude oil hydrocarbons contained an average of 10,000?mg TPH/kg dry soil, these soils had limited hydrocarbon availability, nontoxic conditions, and low potential for chemical migration. For the soils containing the diesel fuel, active prepared bed bioremediation of about 15 weeks was adequate to reach an environmentally acceptable endpoint. At that time, there was little further TPH loss, no Microtox^TM toxicity, and limited hydrocarbon mobility.     

Impact of surrogate selection on risk assessment for total petroleum hydrocarbons

Environmental contamination involving total petroleum hydrocarbons (TPH) is being investigated and remediated at underground storage tanks, tank farms, pipelines, and refineries across the country. Human health and environmental risk play a significant role in decision making at these sites. However, risk assessment for sites contaminated with petroleum products typically is complicated by inadequate information about the composition of TPH present at the site and the physical and chemical properties and toxicity of the components. To address these data gaps, risk assessors can select surrogate compounds to represent the movement of TPH in the environment at the site and toxicity of TPH present at the site. This article illustrates the potential impact of choice of surrogates on risk estimates, which in turn affect remediation costs.     

Remarkable impact of PAHs and TPHs on the richness and diversity of bacterial species in surface soils exposed to long-term hydrocarbon pollution

Nowadays, because of substantial use of petroleum-derived fuels the number and extension of hydrocarbon polluted terrestrial ecosystems is in growth worldwide. In remediation of aforementioned sites bioremediation still tends to be an innovative, environmentally attractive technology. Although huge amount of information is available concerning the hydrocarbon degradation potential of cultivable hydrocarbonoclastic bacteria little is known about the in situ long-term effects of petroleum derived compounds on the structure of soil microbiota. Therefore, in this study our aim was to determine the long-term impact of total petroleum hydrocarbons (TPHs), volatile petroleum hydrocarbons (VPHs), total alkyl benzenes (TABs) as well as of polycyclic aromatic hydrocarbons (PAHs) on the structure of bacterial communities of four different contaminated soil samples. Our results indicated that a very high amount of TPH affected positively the diversity of hydrocarbonoclastic bacteria. This finding was supported by the occurrence of representatives of the α-, β-, γ-Proteobacteria, Actinobacteria, Flavobacteriia and Bacilli classes. High concentration of VPHs and TABs contributed to the predominance of actinobacterial isolates. In PAH impacted samples the concentration of PAHs negatively correlated with the diversity of bacterial species. Heavily PAH polluted soil samples were mainly inhabited by the representatives of the β-, γ-Proteobacteria (overwhelming dominance of Pseudomonas sp.) and Actinobacteria.     

Incremental sampling methodology for petroleum hydrocarbon contaminated soils: volume estimates and remediation strategies

Current environmental assessments for petroleum hydrocarbon (PHC) contaminated sites are dependent on discrete soil sampling to estimate the degree and extent of contamination, leading to unreliable and non-reproducible results. Incremental sampling methodology (ISM) involves collecting and combining samples within a targeted area and holds promise for being a cost-effective, representative, and reproducible sampling strategy for contaminated site characterization. We hypothesized that traditional Phase II Environmental Site Assessments (ESA) discrete and ISM sampling protocols were not mutually exclusive, and the two approaches can be used to formulate a responsible land management strategy. Results gathered through ISM were compared to those from Phase II ESA for two PHC contaminated sites in Canada. Both methods indicated the sites were impacted with PHC beyond Saskatchewan Tier I guidance, however, the delineation of the PHC plume differed by as much as 75% for the heavier hydrocarbons. The Phase II ESA methods had higher incidences of false positive results and an overestimation of contamination at depth. A laboratory experiment confirmed that ISM does not “dilute” the samples as to cause underestimation, whereby the hydrocarbon concentrations for a single combined sample was equivalent to the mean of 30 discrete samples. Based on our results, sites should undergo risk assessment based on the estimates of the Phase II ESA results using vapor phase logs to estimate contaminant extent. If exposure pathways cannot be eliminated through the risk assessment process, remediation planning based on the ISM results is justified given the demonstrated cost-effectiveness, representativeness, and reproducibility.     

Biostimulation and Phytoremediation Treatment Strategies of Gasoline-Nickel Co-Contaminated Soil

This study investigated the potential effect of poultry dung (biostimulation) and stubborn grass (Sporobolus pyramidalis) (phytoremediation) on microbial biodegradation of gasoline and nickel uptake in gasoline-nickel-impacted soil. In addition, the potential stimulatory effects of nickel on hydrocarbon utilization were investigated over a small range of nickel concentrations (2.5–12.5 mg/kg). The results showed that an increase in nickel concentration increased hydrocarbon degraders in soil by a range of 8.4–17.2% and resulted in a relative increase in gasoline biodegradation (57.5–62.4%). Also, under aerobic conditions, total petroleum hydrocarbons’ (TPH) removal was 62.4% in the natural gasoline-nickel microcosm (natural attenuation), and a maximum of 78.5%, 85.7%, and 95.8% TPH removal was obtained in phytoremediation, biostimulation, and a combination of biostimulation- and phytoremediation-treated microcosms, respectively. First-order kinetics described the biodegradation of gasoline and nickel uptake very well. Half-life times obtained were 28.88, 18.24, 14.44, and 8.56 days for gasoline degradation under natural attenuation, phytoremediation, biostimulation, and combined biostimulation and phytoremediation treatment methods, respectively. The results indicate that these remediation methods have promising potential for effective remediation of soils co-contaminated with petroleum hydrocarbons and heavy metals.     

Effects of Low Temperature and Freeze-Thaw Cycles on Hydrocarbon Biodegradation in Arctic Tundra Soil

Degradation of petroleum hydrocarbons was monitored in microcosms with diesel fuel-contaminated Arctic tundra soil incubated for 48 days at low temperatures (−5, 0, and 7°C). An additional treatment was incubation for alternating 24-h periods at 7 and −5°C. Hydrocarbons were biodegraded at or above 0°C, and freeze-thaw cycles may have actually stimulated hydrocarbon biodegradation. Total petroleum hydrocarbon (TPH) removal over 48 days in the 7, 0, and 7 and −5°C treatments, respectively, was 450, 300, and 600 μg/g of soil. No TPH removal was observed at −5°C. Total carbon dioxide production suggested that TPH removal was due to biological mineralization. Bacterial metabolic activity, indicated by RNA/DNA ratios, was higher in the middle of the experiment (day 21) than at the start, in agreement with measured hydrocarbon removal and carbon dioxide production activities. The total numbers of culturable heterotrophs and of hydrocarbon degraders did not change significantly over the 48 days of incubation in any of the treatments. At the end of the experiment, bacterial community structure, evaluated by ribosomal intergenic spacer length analysis, was very similar in all of the treatments but the alternating 7 and −5°C treatment.     

Naked Amoebas and Bacteria in an Oil-Impacted Salt Marsh Community

Populations of soil amoebas were monitored in two salt marshes in Staten Island, NY for 2 years. One site, Gulfport Reach on the Arthur Kill, has been highly impacted by numerous oil spills. In particular, in 1990 a massive no. 2 fuel oil spill from a ruptured pipe flooded the area; its sediments had total petroleum hydrocarbon (TPH) concentrations in the range 800-46,000 ppm. A reference site 11 km away, on the Atlantic coast, had low TPH levels. Amoeba population densities were in general higher in the impacted sediments. In laboratory microcosm experiments, sediment samples from unimpacted sites were treated with added fresh (unweathered) hydrocarbons (no. 2 fuel oil) and cultured; these also yielded higher amoeba numbers than untreated controls. Four distinct amoeba morphotypes were monitored. Changes in population levels of total amoebas were correlated in the two sites, particularly for morphotype 2 (r = 0.83). The ratios of total amoebas to total bacterial numbers were also correlated (r = 0.85) between the sites. This suggests the amoebas may function as generalists, and that their trophic relation to bacterial prey is not much affected by the presence of petroleum hydrocarbons, but rather may reflect regional parameters such as ambient temperature or other physical factors.     

Background levels of polycyclic aromatic hydrocarbons (PAH) and selected metals in new England urban soils

Polycyclic aromatic hydrocarbons (PAH) are byproducts of combustion and are ubiquitous in the urban environment They are also present in industrial chemical wastes, such as coal tar, petroleum refinery sludges, waste oils and fuels, and wood‐treating residues. Thus, PAHs are chemicals of concern at many waste sites. Risk assessment methods will yield risk‐based cleanup levels for PAHs that range from 0.1 to 0.7 mg/kg. Given their universal presence in the urban environment, it is important to compare risk‐based cleanup levels with typical urban background levels before utilizing unrealistically low cleanup targets. However, little data exist on PAH levels in urban, nonindustrial soils. In this study, 60 samples of surficial soils from urban locations in three New England cities were analyzed for PAH compounds. In addition, all samples were analyzed for total petroleum hydrocarbons (TPH) and seven metals. The upper 95% confidence interval on the mean was 3 mg/kg for benzo(a)pyrene toxic equivalents, 12 mg/kg for total potentially carcinogenic PAH, and 25 mg/kg for total PAH. The upper 95% confidence interval was 373 mg/kg for TPH, which exceeds the target level of 100 mg/kg used by many state regulatory agencies. Metal concentrations were similar to published background levels for all metals except lead. The upper 95% confidence interval for lead was 737 mg/kg in Boston, 463 mg/kg in Providence, and 378 mg/kg in Springfield.     

Treatment of Jet Fuel-Contaminated Runoff Water by Subsurface Infiltration

Subsurface infiltration of jet fuel-contaminated surface runoff from airport activities has been shown to be a feasible treatment method. Complete removal of monoaromatic hydrocarbons and naphthalene was observed in 1-m-long (0.2-m-diameter) soil columns. Mineral soil mixed with 5% peat (MinP) showed the best hydrocarbon removal at variable hydraulic loads (50 to 375 mm/d). Natural mineral soil from the C-horizon (Min) showed good hydrocarbon removal after an initial phase, during which hydrocarbons were found in the leachate. This is believed to be a result of adaptation of the soil microflora to the applied hydrocarbons. When hydrocarbon application was stopped and resumed, a new adaptation phase was observed. Cleaned soil (335 mg/kg total petroleum hydrocarbons [TPH]) from a former diesel-polluted site (MinO) showed good hydrocarbon removal but poor hydraulic conductivity. Removal rates of 4.7 and 3.0 mg/kg/d total hydrocarbons were found for Min and MinP, respectively, over the total column length. The highest removal rates (20 and 18 mg/kg/d total hydrocarbons) are observed in the top 20 cm for Min and MinP. Respectively, Potassium acetate (KAc), used as a deicing chemical on airport runways, caused breakthrough of hydrocarbons in the soil columns. The observed breakthrough was caused by oxygen depletion in MinP and MinO. No oxygen depletion was observed in Min, but substrate competition might have limited the hydrocarbon degradation. Based on the results from this study, a full-scale experimental infiltration plant is being constructed and will be tested during 1997. The full-scale tests will focus on the observed relation between oxygen availability and hydrocarbon removal.     

Biostimulation and bioaugmentation for on-site treatment of weathered diesel fuel in Arctic soil

Bioremediation of weathered diesel fuel in Arctic soil at low temperature was studied both on-site in small-scale biopiles and in laboratory microcosms. The field study site was on Ellesmere Island (82°30'N, 62°20'W). Biostimulation was by fertilization with phosphorous and nitrogen. Bioaugmentation was with an enrichment culture originating from the field site. In biopiles, total petroleum hydrocarbons (TPH) were reduced from 2.9 to 0.5 mg/g of dry soil over a period of 65 days. In microcosms at 7 °C, TPH were reduced from 2.4 to 0.5 mg/g of dry soil over a period of 90 days. Inoculation had no effect on hydrocarbon removal in biopiles or in microcosms. Maximum TPH removal rates in the biopiles were approximately 90 μg of TPH g^–1 of soil day^–1, occurring during the first 14 days when ambient temperature ranged from 0 to 10 °C. The fate of three phylotypes present in the inoculum was monitored using most-probable-number PCR, targeting 16S rRNA genes. Populations of all three phylotypes increased more than 100-fold during incubation of both uninoculated and inoculated biopiles. The inoculum increased the initial populations of the phylotypes but did not significantly affect their final populations. Thus, biostimulation on site enriched populations that were also selected in laboratory enrichment cultures. Electronic Publication