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Directed evolution of new enzymes and pathways for environmental biocatalysis.

Biocatalysis is important in both natural and engineered environments. The major global reactions in the biospheric cycling of carbon, nitrogen, and other elements are catalyzed by microorganisms. The global carbon cycle includes millions of organic compounds that are made by plants, microorganisms, and organic chemists. Most of those compounds are transformed by microbial enzymes. Degradative metabolism is known as catabolism and yields principally carbon dioxide, methane, or biomass. Microbial catabolic enzymes are a great resource for biotechnology. They are the building blocks for engineering novel metabolic pathways and evolving improved enzymes in the laboratory. Two multicomponent bacterial oxygeneases, cytochrome P450cam and toluene dioxygenase, catalyze the dechlorination of polyhalogenated C2 compounds. Seven genes encoding those functional enzyme complexes were coexpressed in a Pseudomonas and shown to metabolize pentachloreothane to nonhalogenated organic acids that were metabolized further to carbon dioxide. In another example, the enzyme catalyzing the dechlorination of the herbicide atrazine was subjected to iterative DNA shuffling to produce mutations. By using a plate screening assay, mutated atrazine chlorohydrolase that catalyzed a more rapid dechlorination of atrazine was obtained. The mutant genes were sequences and found to encode up to 11 amino acid changes. Atrazine chlorohydrolase is currently being used in a model municipal water treatment system to test the feasibility of using enzymes for atrazine decontamination. These data suggest that the natural diversity of bacterial catabolic enzymes provides the starting point for improved biocatalytic systems that meet the needs of commercial applications.

Biodegradation, Environmental↗

Use of both 16S rRNA and engineered functional genes with real-time PCR to quantify an engineered, PCB-degrading Rhodococcus in soil.

A real-time PCR (RTm-PCR) assay using fluorescently labeled oligonucleotides (TaqMan probes) was used to detect and quantify the recombinant Rhodococcus sp. strain RHA1(fcb) in soil. One primer and probe set targeted a hypervariable region of the 16S rRNA gene unique to strain RHA1(fcb) and its phylogenetic relatives, and the other set targeted the recombinant 4-chlorobenzoate (4-CBA) degradation operon (fcb) and was strain-specific. The method had a 6-log dynamic range of detection (10(2)-10(7) cells ml(-1)) for both probes when DNA from pure cultures was used. Although the method was less sensitive in soil, the estimated number of cells in soil by real-time PCR corresponded to the measured number of RHA1(fcb) cells determined by colony-forming units.

Biodegradation, Environmental↗

Biofilm consortia on biomedical and biological surfaces: delivery and targeting strategies.

Microbial biofilms have been observed as congregates and attached communities on a diverse range of microecosystems of medicinal and industrial importance. Until recently, most investigations have been performed on planktonic (floating or fluid phase) microorganisms. After realization of the biofilm existence and their recalcitrance toward conventionally adopted preventive strategies and antimicrobial agents, research has been shifted toward novel therapeutics based drug delivery and targeting approaches. With the emergence of various biofilm models and methods to assess biofilm formation and physiology, it is pivotal to discuss various novel strategies that may become the therapeutic tools and clinically adaptable strategies of the future. This review explores various novel research strategies studied to date for their potential in effective biofilm eradication.

Anti-Bacterial Agents↗

Oxazolidinone resistance mutations in 23S rRNA of Escherichia coli reveal the central region of domain V as the primary site of drug action.

Oxazolidinone antibiotics inhibit bacterial protein synthesis by interacting with the large ribosomal subunit. The structure and exact location of the oxazolidinone binding site remain obscure, as does the manner in which these drugs inhibit translation. To investigate the drug-ribosome interaction, we selected Escherichia coli oxazolidinone-resistant mutants, which contained a randomly mutagenized plasmid-borne rRNA operon. The same mutation, G2032 to A, was identified in the 23S rRNA genes of several independent resistant isolates. Engineering of this mutation by site-directed mutagenesis in the wild-type rRNA operon produced an oxazolidinone resistance phenotype, establishing that the G2032A substitution was the determinant of resistance. Engineered U and C substitutions at G2032, as well as a G2447-to-U mutation, also conferred resistance to oxazolidinone. All the characterized resistance mutations were clustered in the vicinity of the central loop of domain V of 23S rRNA, suggesting that this rRNA region plays a major role in the interaction of the drug with the ribosome. Although the central loop of domain V is an essential integral component of the ribosomal peptidyl transferase, oxazolidinones do not inhibit peptide bond formation, and thus these drugs presumably interfere with another activity associated with the peptidyl transferase center.

Acetamides↗

Simultaneous biodegradation of methyl parathion and carbofuran by a genetically engineered microorganism constructed by mini-Tn5 transposon.

A genetically engineered microorganism (GEM) capable of simultaneous degrading methyl parathion (MP) and carbofuran was successfully constructed by random insertion of a methyl parathion hydrolase gene (mpd) into the chromosome of a carbofuran degrading Sphingomonas sp. CDS-1 with the mini-transposon system. The GEM constructed was relatively stable and cell viability and original degrading characteristic was not affected compared with the original recipient CDS-1. The effects of temperature, initial pH value, inoculum size and alternative carbon source on the biodegradation of MP and carbofuran were investigated. GEM cells could degrade MP and carbofuran efficiently in a relatively broad range of temperatures from 20 to 30 degrees C, initial pH values from 6.0 to 9.0, and with all initial inoculation cell densities (10(5)-10(7) CFU ml(-1)), even if alternative glucose existed. The optimal temperature and initial pH value for GEM cells to simultaneously degrade MP and carbofuran was at 30 degrees C and at pH 7.0. The removal of MP and carbofuran by GEM cells in sterile and non-sterile soil were also studied. In both soil samples, 50 mg kg(-1) MP and 25 mg kg(-1) carbofuran could be degraded to an undetectable level within 25 days even if there were indigenous microbial competition and carbon sources effect. In sterile soil, the biodegradation rates of MP and carbofuran were faster, and the decline of the inoculated GEM cells was slower compared with that in non-sterile soil. The GEM constructed in this study was potential useful for pesticides bioremediation in natural environment.

Biodegradation, Environmental↗

Survival and impact of genetically engineered Pseudomonas putida harboring mercury resistance gene in aquatic microcosms.

The survival of wild-type and genetically engineered Pseudomonas putida PpY101 that contained a recombinant plasmid pSR134 conferring mercury resistance were monitored in aquatic microcosms. We used lake, river, and spring water samples. The density of genetically engineered and wild-type P. putida decreased rapidly within 5 days (population change rate k -0.87 approximately -1.00 day-1), then moderately after 5 to 28 days (-0.10 approximately -0.14 day-1). The population change rates of genetically engineered and wild-type P. putida were not significantly different. We studied the important factors affecting the survival of genetically engineered and wild-type P. putida introduced in aquatic microcosms. Visible light exerted an adverse effect on the survival of the two strains. The densities of genetically engineered and wild-type P. putida were almost constant until 7 days after inoculation in natural water filtered with a 0.45-micron membrane filter, or treated with cycloheximide to inhibit the growth of protozoa. These results suggested that protozoan predation was one of the most important factors for the survival of two strains. We examined the impact of the addition of genetically engineered and wild-type P. putida on indigenous bacteria and protozoa. Inoculation of genetically engineered or wild-type P. putida had no apparent effect on the density of indigenous bacteria. The density of protozoa increased in microcosms inoculated with genetically engineered or wild-type P. putida at 3 days after inoculation, but after 5 to 21 days, the density of protozoa decreased to the same level as the control microcosms.

Animals↗

Escherichia coli engineered to produce eicosapentaenoic acid becomes resistant against oxidative damages.

The colony-forming ability of Escherichia coli genetically engineered to produce eicosapentaenoic acid (EPA) grown in 3mM hydrogen peroxide (H(2)O(2)) was similar to that of untreated cells. It was rapidly lost in the absence of EPA. H(2)O(2)-induced protein carbonylation was enhanced in cells lacking EPA. The fatty acid composition of the transformants was unaffected by H(2)O(2) treatment, but the amount of fatty acids decreased in cultures of cells lacking EPA and increased in cultures of cells producing EPA, suggesting that cellular EPA is stable in the presence of H(2)O(2) in vivo and may protect cells directly against oxidative damage. We discuss the possible role of EPA in partially blocking the penetration of H(2)O(2) into cells through membranes containing EPA.

Catalase↗

Use of genetically engineered Escherichia coli to monitor ingestion, loss, and transfer of bacteria in termites.

Escherichia coli was transformed with a recombinant plasmid (pEGFP) containing the genes for ampicillin resistance and Green Fluorescent Protein (GFP). Escherichia coli expressing GFP (E. coli/GFP+) was then fed to workers of the termite Coptotermes formosanus Shiraki (Isoptera: Rhinotermitidae). The transformed bacteria in the termite guts were detected by growing the gut flora under selective conditions and then checking the cultures for fluorescence. Recombinant plasmids in the termite gut were detected by plasmid extraction with subsequent restriction enzyme digest. The presence of the GFP gene in the gut of termites fed with E. coli/GFP+ was verified by PCR amplification. Transformed E. coli were ingested rapidly when workers fed on filter paper inoculated with E. coli/GFP+. After 1 day, 42% of termite guts harbored E. coli/GFP+. Transfer of E. coli/GFP+ from donor termites (fed with E. coli/GFP+) to recipients (fed with moist filter paper) occurred within 1 day. However, without continuous inoculation, termites lost the transformed bacteria within 1 week.

Ampicillin Resistance↗

A decision support system for the prediction of microbial food safety and food quality.

The development of a method to predict microbial food safety and quality is described. The manufacture of a food from its ingredients is simulated, using a recipe. Food engineering heuristics are combined with models developed in predictive microbiology. Parameter values of ingredients of foods, such as water activity and pH, and models for microbial growth and decay are used for the prediction of the kinetics of microorganisms generally found in ingredients. The values of these parameters are collected in databases. If required information is lacking, methods are described for making reliable guesses of the parameters. Food quality can be calculated as a function of fluctuating temperature in time. Several food distribution chains can be simulated in order to assess the influence of distribution chains on food quality. The described methods were implemented into a computerised decision support system that can be used in food production, product development and training. In the future it may be possible to apply specific expert knowledge in production and development of foods to improve the quality of prediction.

Animals↗

Distribution of a genetically-engineered Escherichia coli population introduced into soil.

The spatial localization of the cells and the DNA of a genetically-engineered Escherichia coli population introduced into soil was investigated. Inoculated soils were size fractioned and bacterial numbers and E. coli EL1003 specific chromosomal DNA target sequences were enumerated in each fraction using plate-counting and MPN-PCR, respectively. Different numbers of either indigenous or introduced bacteria were found in each fraction indicating that their distribution in the soil was non-uniform. The distributions of the indigenous bacteria and the E. coli cells within the size fractions were significantly different: the E. coli population was mainly associated with the dispersible clay fraction (79.0%) from which only 10.7% of the indigenous bacteria were recovered. The distribution of the E. coli target DNA sequences was in agreement with the location of the cells. The different distribution of the two populations is likely to restrict genetic interactions. These results are relevant to potential interactions between native soil microflora and populations introduced into soil for competitive purposes.

Bacteria↗

(M)VOC and composting facilities. Part 1: (M)VOC emissions from municipal biowaste and plant refuse.

GOAL, SCOPE AND BACKGROUND: Malodorous volatiles derived from the decomposition of biowaste within the process of composting might pose a risk to human health. Different techniques of process engineering have been developed to minimise the burden of malodorous compounds in air possibly affecting compost workers and residents in the vicinity. METHODS: In the present study, three different composting facilities were examined for the emission of volatiles to estimate the impact of process engineering on the dispersal of odorous compounds and to discuss its relevance for human health. RESULTS AND DISCUSSION: Concentrations of single compounds belonging to alcohols, ketones, furanes, sulfur-containing compounds and especially terpenes ranged from 10(2) up to nearly 10(6) ng/m3 depending on the sampling sites and the process engineering. The ratio of MVOC and total VOC measured changed throughout the process of biodegradation. A certain combination of volatile compounds coincided with the occurrence of typical compost odour. CONCLUSION: The type of process engineering seemed to have a major impact on the emission of volatiles, as amounts of (microbial) volatiles emitted were characteristic for the different techniques used. Thus, the MVOC emission basically depends on the degree of biodegradation. It is likely that the concentrations workers are exposed to can have an impact on human health. RECOMMENDATIONS AND OUTLOOK: It is obvious that less sophisticated types of process engineering give rise to greater amounts of bioaerosols and volatiles and, therefore, technical devices have to be improved and controlled regularly to minimise adverse health effects on workers.

Bioreactors↗

[Experimental study of bone infection on WO-1 controlled-release system].

OBJECTIVE: To develop a new tissue engineering bone material which has an anti-infective function. METHODS: Collagen loaded bio-derived bone material was made by using type-I collagen and allograft bone. WO-1 was absorbed to collagen loaded bio-derived bone, then the morphological feature of the new bone material was observed by scanning electronic microscopy. 3H-tetracycline was diluted by WO-1 solution, and was absorbed to collagen loaded bio-derived bone, then the releasing kinetics of WO-1 was detected by 3H-tetracycline in vitro. WO-1 bio-derived bone material was grafted into a culture medium with staphylococcus aureus, Escherichia coli, and pseudomonas aeruginosa to observe its bacteriostasis ability. WO-1 bio-derived bone material was grafted into radius of defected rabbits, the concentration of WO-1 was detected on the 9th, 16th, 23th, and 30th day by HLPC in blood, in bone and in muscle. The bacteriostasis ability of WO-1 loaded bio-derived bone was tested in vitro and in vivo. RESULTS: WO-1 loaded bio-derived bone maintained natural network pore system and the surface of network pore system was coated with collagen membrane. The release of WO-1 from WO-1 loaded bio-derived bone showed bursting release on the 1st day, then showed stable release. WO-1 loaded bio-derived bone showed lasting and stable bacteriostasis to common pathogens of orthopaedic infections. The high concentration of WO-1 was observed in bone tissue and in muscle tissue at different time points and the difference among groups had no significance (P>0.05), while the concentration of WO-1 in blood was very low (P<0.05). CONCLUSION: WO-1 loaded bio-derived bone has good capability of drug controlled-release and bacteriostasis.

Animals↗

Engineered passive bioreactive barriers: risk-managing the legacy of industrial soil and groundwater pollution.

Permeable reactive barriers are a technology that is one decade old, with most full-scale applications based on abiotic mechanisms. Though there is extensive literature on engineered bioreactors, natural biodegradation potential, and in situ remediation, it is only recently that engineered passive bioreactive barrier technology is being considered at the commercial scale to manage contaminated soil and groundwater risks. Recent full-scale studies are providing the scientific confidence in our understanding of coupled microbial (and genetic), hydrogeologic, and geochemical processes in this approach and have highlighted the need to further integrate engineering and science tools.

Bacteria↗

[Preparation of functioning recombinant (hybrid) DNA molecules in vitro (genetic engineering experiments)].

In this paper we describe the preparation of hybrid plasmid consisting of ColE1 DNA and DNA of R6K plasmid. ColE1 plasmid represents a circular DNA with the molecular weight of 4,2-10(6) daltons. It determines colicine synthesis E1, has relaxed control of replication and is present in the cell in several dozens copies. Transmissive plasmid B6K represents a circular DNA molecule with the molecular weight of 28-10(6) daltons. It confers the resistance to amplicillin and streptomycin and belongs to the compatibility group X. This plasmid also has relaxed control of replication (up to 30 copies per cell). Circular superhelical DNA of ColE1 was prepared after it is amplification with cloramphenicol according to Clewell by ultracentrifugation in CsCl-EtBr density gradient. The yield of superhelical ColE1 DNA in our experiments was up to 300 mg/gram cells. Circular superhelical R6K DNA was isolated from E. coli strain J53 R6K grown to stationary phase in the presence of 15 mg/ml of streptomycin. The yield of superhelical DNA was equal to about 45 mg per 1 gram cells. EcoR1 restrictase was prepared from E. coli KM182 as described by Thomas et al. From 37 grams of cells 10 ml of enzyme solution was prepared. 1 ml of this solution was able to restrict completely 2 mg of ColE1 DNA during Hu incubation for 30 degrees min at 37 degrees C. Restrictase activity was analyzed by electrophoresis of ColE1 DNA restricts in 0,7% agarose gel as described by Tanaka. DNA ligase was prepared from E. coli B. cells infected by T4 phage am81 mutant as described by Weiss. The activity of enzyme solution was equal to 90 units/ml (according to Richardson). In standard "hybridization" experiment 4 mug of ColE1 DNA and 4 mug of R6K DNA were incubated for 1 hour at 37 degrees in 0,2 ml of the solution containing 40 mM tris-HCl, pH 7,4; 10 mM MgCl2 50 mM NaCl, 10 mM mercaptoethanol and 5 mul of EcoR1 restrictase. The reaction was terminated by heating the reaction mixture to 65 degrees C for 5 min. In accordance with the results of others CoLE1 DNA gave one restrict and R6K DNA-two restricted fragments. 100 mul of the restricted mixture was chilled to 0 degrees and the following ingredients were added 10 mul of 50 mM MgCl2; 10 mul of 100 mM dithiotreitol; 10 mul of 0,5 mM ATP, 20 mul of water and 8 mul of ligase solution (90 units/mul). The mixture was incubated at 0-0,5 degrees for 53 hours, thereafter it was used for the transformation of E. coli C600 according to Tanaka et al. Several classes of hybrid molecules due to different combinations of restricted fragments of parental species were expected. These molecules had to confer the immunity to colicine E1 and to carry the defect in the gene controlling colicine synthesis since EcoR1 restrictase splits ColE1 DNA in the region of corresponding gene. In addition, certain classes of transformants with hybrid DNA molecules had to be resistant to one or both antibiotics as determined by the R6K plasmid portion...

Colicins↗

Solution hybridization assay for detecting genetically engineered microorganisms in environmental samples.

A solution hybridization method was developed for detecting genetically engineered microorganisms in environmental samples. The detection method involves recovery of DNA from the microbial community of an environmental sample followed by hybridization in solution with a radiolabeled RNA gene probe. After nuclease digestion of non-hybridized probe RNA, the DNA-RNA hybrids formed in the solution hybridization reaction are separated by sephadex or hydroxyapatite column chromatography and detected by liquid scintillation counting. Using solution hybridization-gene probe detection, as few as 100-1000 target cells per gram sediment sample of a 2,4,5-T-degrading genetically engineered microorganisms could be detected.

Chromatography, Gel↗

Microbiological profiles of four Apollo spacecraft.

Selected surfaces from the Command Module, Lunar Module (ascent and descent stages), Instrument Unit, Saturn S-4B engine, and Spacecraft Lunar Module Adapter comprised the various components of four Apollo spacecraft which were assayed quantitatively and qualitatively for microorganisms. In addition, the first Lunar Roving Vehicle was assayed. Average levels of microbial contamination (10(4) per square foot of surface) on the Command Module, Instrument Unit, and Saturn S-4B engine were relatively consistent among spacecraft. The first postflight sampling of interior surfaces of the Command Module was possible due to elimination of the 21-day back-contamination quarantine period. Results of the pre- and postflight samples revealed increases in the postflight samples of 3 logs/inch(2). A total of 5,862 microbial isolates was identified; 183 and 327 were obtained from the Command Module at preflight and postflight sampling periods, respectively. Although the results showed that the majority of microorganisms isolated were those considered to be indigenous to humans, an increase in organisms associated with soil and dust was noted with each successive Apollo spacecraft.

Actinomycetales↗

The essential role of hydrodynamic shear force in the formation of biofilm and granular sludge.

Biofilm and granular sludge processes are promising biotechnology for wastewater treatment. The formation, structure and metabolism of immobilized microbial community are associated very closely with hydrodynamic shear force in reactors. Therefore, this paper attempts to review the essential role of shear force in the formation and performance of biofilm and granular sludge. More compact, stable and denser biofilms, aerobic and anaerobic granules form at relatively higher hydrodynamic shear force. It is clearly shown that shear force has significant influences on the structure, mass transfer, production of exopolysaccharides, metabolic/genetic behaviours of biofilms, aerobic and anaerobic granules. In an engineering sense, hydrodynamic shear force can be manipulated, as a control parameter, to enhance microbial granulation process. It can be concluded that the knowledge regarding the effects of hydrodynamic shear force on biofilms and granules is far from complete and much research is still needed to fully understand the relevant mechanisms. Some of these future research niches are therefore outlined.

Biofilms↗

Novel pristinamycin-responsive expression systems for plant cells.

Novel gene regulation systems were designed for plant cells responsive to the streptogramin antibiotic pristinamycin. The pristinamycin-repressible plant gene regulation concept (PIPpOFF) is based on a transcriptional activator (PIT) which consists of the Pip protein, the repressor of the pristinamycin resistance operon of Streptomyces coelicolor, fused to the VP16 transactivation domain of the Herpes simplex virus. PIT mediates pristinamycin-repressible activation of a synthetic plant promoter (P(pPIR)) in tobacco cells consisting of a nine Pip-binding site-containing artificial operator (PIR3) placed upstream of a TATA-box derived from the cauliflower mosaic virus 35S promoter (P(CaMV35S)). Pristinamycin interferes with induction by negatively regulating the DNA-binding capacity of the Pip moiety of PIT. A second, streptogramin-inducible plant gene regulation system (PIPpON) was constructed by combining Pip expression with a plant-specific pristinamycin-inducible promoter (P(pPIRON)). P(pPIRON) consists of a PIR3 module cloned downstream of the strong constitutive plant promoter P(CaMV35S). As in the native Streptomyces configuration, Pip binds to its cognate sequence within P(pPIRON) in the absence of regulating antibiotic and silences the chimeric plant promoter. Upon addition of pristinamycin, Pip is released from the PIR3 operator and full P(CaMV35S)-driven expression of desired plant genes is induced. The PIPpOFF and PIPpON systems performed well in Nicotiana tabacum suspension cultures and promise to provide an attractive extension of existing plant gene regulation technology for basic plant research or biopharmaceutical manufacturing using plant tissue culture.

Amino Acid Sequence↗