<p>Chlorinated solvents are common contaminants in soil and water. Under anaerobic conditions microbes are capable of transforming chlorinated solvents into ethylene which would result in a remediation of the contaminated area. In order to use natural attenuation as a remediation method evidence of continuous degradation is required. Furthermore, the degradation must occur at a sufficient rate and continuous monitoring of the site is needed until the demanded levels are achieved. A field study was performed on the basis of data from a dry-cleaning facility contaminated mainly by perchloroethylene. The purpose of the study was to define the existing situation regarding distribution and transformation of contaminant in order to evaluate the possibilities of using natural attenuation as a method of remediation. Degradation of perchloroethylene proceeds through successive removal of chlorine, with the formation of trichloroethylene, dichloroethylene, vinyl chloride and ethylene. There exists evidence of degradation as far as vinyl chloride on the site but whether transformation continues to ethylene is not established. The computer model Biochlor was used to simulate distribution and degradation of the contaminants. The site possesses a complex hydrogeology and the existing data are not sufficient to distinguish the effect of degradation from other factors such as spreading of contaminant between different layers of soil. Since degradation failed to be quantified, natural attenuation can not be recommended as a safe remediation method at the considered site without further investigations.</p> / <p>Klorerade lösningsmedel är vanligt förekommande föroreningar i mark och vatten. Under anaeroba förhållanden kan mikrober omvandla klorerade kolväten till eten vilket leder till rening av det förorenade området. För att kunna använda denna naturliga nedbrytning som saneringsmetod krävs bevis för att nedbrytning fortskrider i tillräcklig utsträckning för att rena området och därefter krävs kontinuerlig provtagning till dess målen för saneringen har uppnåtts. En fallstudie utfördes utifrån data från en kemtvättsfastighet förorenad av i första hand perkloreten. Syftet var att kartlägga föroreningssituationen med avseende på spridning och nedbrytning av de klorerade föreningarna för att undersöka om naturlig nedbrytning var en möjlig framtida saneringsmetod. Nedbrytning av perkloreten sker stegvis genom att klor avspjälkas, under bildande av produkterna trikloreten, dikloreten, vinylklorid och etengas. Nedbrytning av förorening har konstaterats ske på fastigheten fram till vinylklorid men huruvida nedbrytning avstannat där eller fullföljts till etengas är ej klarlagt. Datormodellen Biochlor användes för att simulera spridning och nedbrytning av utsläppet. Fältplatsen har en komplex hydrogeologi och befintliga fältdata var inte tillräckliga för att särskilja nedbrytningens effekt från faktorer såsom spridning av förorening mellan olika jordlager. Eftersom nedbrytningen inte kunde kvantifieras kan naturlig nedbrytning inte rekommenderas som säker saneringsmetod på denna fältplats utan kompletterande analyser.</p>

No description available.

The aim of this study was to assess the performance of thermal heating for the removal of chlorinated solvents from fractured rock. The study included a laboratory experimental program, a field pilot study demonstration and a mathematical modeling component. In the laboratory experimental program, thermal heating parameters, such as operational temperature, heating duration, and the corresponding degree of contaminant removal, were evaluated through a series of heating tests. To evaluate the effect of heating temperature and heating duration on the degree of contaminant mass removal, two different heating profiles were utilized during the experiments. Additionally, seven types of rock and two common contaminants were selected to evaluate the effect of thermal heating on different geological media impacted with different chlorinated compounds. In general, results showed that heating duration had the most significant effect on the degree of contaminant mass removal in post-remedy samples. Results showed that a higher porosity in combination with a lower organic content facilitates the removal of chlorinated solvents from the rock matrix. A Thermal Conductive Heating (TCH) pilot test was implemented by TerraTherm, Inc. at the former Naval Air Warfare Center (NAWC) in West Trenton, NJ to assess the performance of TCH for the removal of trichloroethylene (TCE) and daughter products (i.e cis-1,2-dichloroethylene (DCE) and vinyl chloride (VC)) from fractured bedrock. Results showed that treatment removed 318.5 kg of TCE, DCE and VC, from the treatment zone, of which 62.6 kg were recovered from the rock matrix. A total of 63 % TCE, 65.8 % of DCE and 90.4% of VC were removed during heating. Finally, Semi-analytical solutions were derived to evaluate back diffusion in a fractured bedrock environment where the initial condition comprises a spatially uniform, non-zero matrix concentration throughout the domain. It was concluded that the time required to reach a desired fracture pore water concentration is a function of the distance between the point of compliance and the upgradient face of the domain where clean groundwater is inflowing. Hence, shorter distances correspond to reduced times required to reach compliance. / Thesis (Ph.D, Civil Engineering) -- Queen's University, 2012-09-24 11:30:16.52

This study evaluates the effectiveness of molasses injection for reducing heavy metals and chlorinated solvents in a ground water plume at the Avco-Lycoming Superfund site in Williamsport, Pennsylvania. Molasses injection stimulates the respiration of microorganisms to make a more reducing environment. As the environment?s Redox potential decreases, the rate of chemical reduction increases. The concentrations of heavy metals and chlorinated solvents were monitored to evaluate the effectiveness of the molasses injection. The statistics revealed a decrease in the Oxidation-Reduction Potential in the groundwater and a reduction in hexavalent chromium and TCE concentrations in the groundwater. The Environmental Protection Agency views molasses injection as a viable technique for site remediation. Molasses injection is a form of facilitated natural attenuation. Molasses is injected into a plume to make the environment anaerobic. An anaerobic environment facilitates the microbes that breakdown trichloroethylene (TCE), trans-dichloroethylene (DCE), vinyl chloride (VC) and hexavalent chromium.

Chlorinated solvents are among the most prevalent contaminants at Superfund sites. Perchloroethylene (PCE) and its degradative byproducts pose a particular problem because of their persistence in the subsurface and their threat to ecological health. In this study, microcosms were used to test the viability of bioaugmentation as a possible remediation strategy at a PCE contaminated site at the Naval Amphibious Base at Little Creek located in Virginia Beach, Virginia. All microcosms were created in duplicate using spatially diverse soils and the bioaugmented series innoculated with a mixed microbial culture provided by the Dr. Frank Loffler. This culture has been found to be capable of completely degrading PCE to ethene. The aqueous ethene concentration was monitored over time. It is clear from the results that bioaugmentation successfully increased the degree of reductive dechlorination over their static counterpart. Without innoculation, shallow static microcosms showed an accumulation of cis-DCE, while deep soils never showed conversion beyond TCE. Shallow bioaugmented microcosms showed the production and loss of vinyl chloride indicated probable complete conversion of PCE to ethene while deep soils showed the production of cis-DCE. These differences in dechlorination between shallow and deep soils indicate a possible disparity in reduction capacity. At day 78, microcosms were spiked with higher concentrations of PCE resulting in a reduction in dechlorination activity. Static microcosms exhibited similar degradative trends but bioaugmented batches experienced dramatic reductions in dechlorination activity indicating possible inhibition effects of native organisms due to concentration or potential toxic shock. It appears that bioaugmentation is a remediation alternative worthy of further study including possible delivery methods, toxicity or inhibition effects of concentration, and fate/transport studies. / Master of Science

Västerås is a city with an industrial heritage. One of the larger companies in Västerås is ABB AB, which has multiply businesses located at the area Finnslätten. High concentrations of trichloroethene (TCE) were found in the soil and groundwater at Finnslätten 1 during a phase II environmental site assessment. Due to the result of the assessment a supplementary investigation and a site specific risk assessment were made of building 358. The source zone and plume of trichloroethene have not been characterized even after several investigations at the site. The aim of this study was to make a risk assessment of three other buildings inside the area were degreasing with TCE have historical taken place. The collected information resulted in a risk class 2 of the three objects and shows that the buildings might be potential pre-emission sources of trichloroethene. The second aim contains a comparison between traditional and alternative approaches to enlighten the importance of effective characterization methods. Two potential characterization strategies were chosen; TRIAD approach and CMF approach. The result showed the importance of systematic project planning, dynamic work planning strategy and the use of multiple techniques to form the best “hybrid” during characterization of DNAPL. In order to bring the investigation to a successful conclusion it is of great importance to consider the uncertainties or diminish the uncertainties by collecting essential information.

Bioremediation of chlorinated contaminants in groundwater can be achieved by reductive dechlorination by anaerobic dechlorinating cultures. However, at sites impacted with multiple different chlorinated contaminants, reductive dechlorination is often inhibited by co-contaminants. The inhibitory effects of trichloroethene, cis-dichloroethene and vinyl chloride on chloroform dechlorination were studied using a Dehalobacter-containing chloroform dechlorinating mixed culture (ACT-3). The inhibitory effect of chloroform on chlorinated ethene dechlorination was studied in a Dehalococcoides-containing trichloroethene dechlorinating mixed culture (KB-1). Vinyl chloride was found to be the strongest inhibitor of chloroform in ACT-3. Chloroform exerted a complex and strong inhibitory effect on chlorinated ethene dechlorination in KB-1. The potential for microbial reductive defluorination was also examined in the enrichment cultures. Quantifying the substrates and substrate interactions in dechlorinating cultures is necessary to most efficiently use these cultures to remediate contaminated sites.

Bioremediation of chlorinated contaminants in groundwater can be achieved by reductive dechlorination by anaerobic dechlorinating cultures. However, at sites impacted with multiple different chlorinated contaminants, reductive dechlorination is often inhibited by co-contaminants. The inhibitory effects of trichloroethene, cis-dichloroethene and vinyl chloride on chloroform dechlorination were studied using a Dehalobacter-containing chloroform dechlorinating mixed culture (ACT-3). The inhibitory effect of chloroform on chlorinated ethene dechlorination was studied in a Dehalococcoides-containing trichloroethene dechlorinating mixed culture (KB-1). Vinyl chloride was found to be the strongest inhibitor of chloroform in ACT-3. Chloroform exerted a complex and strong inhibitory effect on chlorinated ethene dechlorination in KB-1. The potential for microbial reductive defluorination was also examined in the enrichment cultures. Quantifying the substrates and substrate interactions in dechlorinating cultures is necessary to most efficiently use these cultures to remediate contaminated sites.

No description available.

No description available.