Rapid method for the detection of genetically engineered microorganisms by polymerase chain reaction from soil and sediments

A rapid and sensitive method for the detection of genetically engineered microorganisms in soil and sediments has been devised by in vitro amplification of the target DNAs by a polymerase chain reaction. A cloned catechol 2,3-dioxygenase gene located on the recombinant plasmid pOH101 was transferred to Pseudomonas putida MMB2442 by triparental crossing and used as a target organism. For the polymerase chain reaction from soil and sediment samples, the template DNA was released from a 100-mg soil sample. Bacterial seeded soil samples were washed with Tris-EDTA buffer (pH 8.0) and treated with a detergent lysis solution at 100°C. After addition of 1% polyvinylpolypyrrolidine solution, the samples were boiled for 5 min. Supernatant containing nucleic acid was purified with a PCR purification kit. The purified DNA was subjected to polymerase chain reaction, using two specific primers designed for the amplification of catechol 2,3-dioxygenase gene sequences. The detection limit was 10² cells per gram of soil. This method is rapid and obviates the need for lengthy DNA purification from soil samples. Received 28 February 1997/ Accepted in revised form 23 November 1997     

受水杨酸盐浓度调控的细菌遏制系统

由于存在基因工程微生物(GEMs)不受控制地在环境中释放的风险, 利用GEMs的生物降解能力治理环境污染的方法受到了限制。在大肠杆菌JM109中构建了一个受环境污染物调控的细菌遏制系统, 该系统是由杀伤元件和调控元件组成的双质粒体系, 使细菌的存活受环境中水杨酸盐浓度的调控。当培养基含水杨酸盐时, 阻遏蛋白LacI合成, 阻止自杀基因gef表达, 细菌快速繁殖; 当水杨酸盐不存在时, 自杀基因gef的表达导致细胞杀伤, 菌体大量死亡。该遏制系统可作为模型用于具有生物修复功能的基因工程菌的构建。     

Conceptualizing "suicidal genetically engineered microorganisms" for bioremediation applications

Use of genetically modified microorganisms (GEMs) for pollution abatement has been limited because of risks associated with their release in the environment. Recent developments in the area of recombinant DNA technologies have paved the way for conceptualizing "suicidal genetically engineered microorganisms" (S-GEMS) to minimize such anticipated hazards and to achieve efficient and safer bioremediation of contaminated sites. Our strategy of designing a novel S-GEM is based on the knowledge of killer-anti-killer gene(s) that would be susceptible to programmed cell death after detoxification of any given contaminated site(s).     

Crossing the divide: gene flow produces intergeneric hybrid in feral transgenic creeping bentgrass population

Gene flow is the most frequently expressed public concern related to the deregulation of transgenic events ( Snow 2002 ; Ellstrand 2003 ). However, assessing the potential for transgene escape is complex because it depends on the opportunities for unintended gene flow, and establishment and persistence of the transgene in the environment ( Warwick et al. 2008 ). Creeping bentgrass (Agrostis stolonifera L.), a turfgrass species widely used on golf courses, has been genetically engineered to be resistant to glyphosate, a nonselective herbicide. Outcrossing species, such as creeping bentgrass (CB), which have several compatible species, have greater chances for gene escape and spontaneous hybridization (i.e. natural, unassisted sexual reproduction between taxa in the field), which challenges transgene containment. Several authors have emphasized the need for evidence of spontaneous hybridization to infer the potential for gene flow ( Armstrong et al. 2005 ). Here we report that a transgenic intergeneric hybrid has been produced as result of spontaneous hybridization of a feral‐regulated transgenic pollen receptor (CB) and a nontransgenic pollen donor (rabbitfoot grass, RF, Polypogon monspeliensis (L.) Desf.). We identified an off‐type transgenic seedling and confirmed it to be CB × RF intergeneric hybrid. This first report of a transgenic intergeneric hybrid produced in situ with a regulated transgenic event demonstrates the importance of considering all possible avenues for transgene spread at the landscape level before planting a regulated transgenic crop in the field. Spontaneous hybridization adds a level of complexity to transgene monitoring, containment, mitigation and remediation programmes.     

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.     

Use of Genetically Engineered Microorganisms (GEMs) for the Bioremediation of Contaminants

ABSTRACT

This paper presents a critical review of the literature on the application of genetically engineered microorganisms (GEMs) in bioremediation. The important aspects of using GEMs in bioremediation, such as development of novel strains with desirable properties through pathway construction and the modification of enzyme specificity and affinity, are discussed in detail. Particular attention is given to the genetic engineering of bacteria using bacterial hemoglobin (VHb) for the treatment of aromatic organic compounds under hypoxic conditions. The application of VHb technology may advance treatment of contaminated sites, where oxygen availability limits the growth of aerobic bioremediating bacteria, as well as the functioning of oxygenases required for mineralization of many organic pollutants. Despite the many advantages of GEMs, there are still concerns that their introduction into polluted sites to enhance bioremediation may have adverse environmental effects, such as gene transfer. The extent of horizontal gene transfer from GEMs in the environment, compared to that of native organisms including benefits regarding bacterial bioremediation that may occur as a result of such transfer, is discussed. Recent advances in tracking methods and containment strategies for GEMs, including several biological systems that have been developed to detect the fate of GEMs in the environment, are also summarized in this review. Critical research questions pertaining to the development and implementation of GEMs for enhanced bioremediation have been identified and posed for possible future research.     

Nitrification and denitrification: Probing the nitrogen cycle in aquatic environments

Methods designed to detect microorganisms involved in the biogeochemistry of nitrogen in the marine environment are rapidly being developed and deployed in ecological investigations. Probes based on phylogenetic sequences (usually rRNA) and those based on the sequences of functional genes or proteins have both been demonstrated in the nitrogen cycle. The most progress has been made for ammonia oxidizers; several sets of PCR primers have been described and their specificity may be optimized to allow detection of genetically and ecologically meaningful groups. For denitrifying bacteria, functional probes based on nitrite reductase show most promise. These approaches should complement the more familiar, but no less sophisticated, methods that focus on quantification of in situ transformation rates. Both approaches in combination will be useful in understanding regulation and environmental control of biogeochemical processes. Correspondence to: B.B. Ward     

Methods for detecting recombinant DNA in the environment

The successful introduction of genetically modified and genetically engineered microorganisms into the environment requires a quantitative evaluation of the survival and dispersion of the microorganisms and specific gene(s) in the environment. The objective of this article is to examine the applicability, suitability, and significance of existing and new methods for detecting and monitoring the recombinant genes or organisms introduced into the environment. Conventional microbiological method(s) involving the selective and differential growth of microorganism(s) adn other quantitative approaches such as the most-probable-number (MPN) method and direct microscopic observation (e.g., acridine orange direct count analysis) have drawbacks and are not specific or universally applicable. Direct enumeration by immunofluorescence by the use of fluorescent dye seems more sensitive although still not perfect. However, the molecular methodologies such as the use of gene probes, plasmid epidemiology, antibiotic resistant marker strains, and protein electrophoresis and bacteriophage sensitivity are receiving more attention. As yet, the technology of DNA:DNA hybridization appears to be very useful, sensitive, and accurate for detecting and monitoring the microorganisms in the environment, although improvements are required. New approaches can be developed which may include biochemical signature compounds as well as gene cassettes to be used in a complementary fashion with conventional and molecular techniques for quantifying specific genotypes and genes in the environment.     

Bacterial genotoxicity bioreporters

Ever since the introduction of the Salmonella typhimurium mammalian microsome mutagenicity assay (the ‘Ames test’) over three decades ago, there has been a constant development of additional genotoxicity assays based upon the use of genetically engineered microorganisms. Such assays rely either on reversion principles similar to those of the Ames test, or on promoter–reporter fusions that generate a quantifiable dose-dependent signal in the presence of potential DNA damaging compounds and the induction of repair mechanisms; the latter group is the subject of the present review. Some of these assays were only briefly described in the scientific literature, whereas others have been developed all the way to commercial products. Out of these, only one, the umu-test, has been fully validated and ISO- and OECD standardized. Here we review the main directions undertaken in the construction and testing of bacterial-based genotoxicity bioassays, including the attempts to incorporate at least a partial metabolic activation capacity into the molecular design. We list the genetic modifications introduced into the tester strains, compare the performance of the different assays, and briefly describe the first attempts to incorporate such bacterial reporters into actual genotoxicity testing devices.     

A review of available systems to investigate transfer of DNA to indigenous soil bacteria

The deliberate or accidental release of genetically engineered microorganisms (GEMs) in the environment has led to some questions concerning microbial survival, transfer of DNA to the indigenous microflora and environmental consequences. Amongst horizontal gene transfer mechanisms, conjugation is probably the most frequent in the environment. With the aim of evaluating risks associated with environmental release of GEMs and their engineered DNA, studies of conjugative gene transfer between a donor strain and indigenous microflora have been conducted. Such studies required the development of a donor counterselection system to prevent growth of donor cells on transconjugant selective plates. This review summarizes the known and potential donor counterselection systems.     

Containment in industrial biotechnology within wastewater treatment plants

Both physical and biological containment are considered to be essential parts in the risk analysis of industrial Good Industrial Large-Scale Practice (GILSP) processes using genetically modified organisms (GMOs). Biological containment of industrial microorganisms has become a more important issue since the introduction of recombinant DNA techniques. In the event of an accidental discharge in the production plant, a large amount of organisms could be released into the wastewater treatment (WWT) system. This WWT system should therefore be considered as a part of the containment. This study demonstrates both a hydrodynamic and a microbiological model for the containment aspects of industrial WWT plants. The models are verified by measurements using industrial hosts of GILSP GMOs at full scale. Both models describe the full-scale equipment accurately. The results are supplemented with microcosm studies on survival of GMOs in defined niches. It is shown that WWT plants can be considered as useful additional parts of the containment of microorganisms, in case of an accidental discharge. The effect of drainage of an enormous amount of microorganisms (several tons) through the WWT plant into the environment is shown to be comparable to the direct drainage of a small-scale fermenter. Microcosm experiments correlate well with the survival rates in the WWT and therefore can be of use to predict the behaviour of GMOs in this environment. Journal of Industrial Microbiology & Biotechnology (2002) 28, 65–69 DOI: 10.1038/sj/jim/7000210 Received 16 July 2001/ Accepted in revised form 05 September 2001     

Methods of assessment of transfer of a gentamycin-resistance gene (aacC1) from genetically engineered microorganisms into agriculturally important soil bacteria

In order to assess the risk associated with the deliberate release of genetically engineered microorganisms (GEMs) into the agricultural environment, the transfer of plasmids between bacterial strains was investigated under laboratory conditions. Genetically modified Rhizobium leguminosarum and Agrobacterium tumefaciens strains carrying the gentamycin acetyltransferase resistance gene (aacC1) on various plasmids were investigated for their ability to transfer the aacC1 gene to their wild-type (w.t.) counterparts, as well as to Pseudomonas syringae. Conjugation experiments between the various strains, were carried out after the relevant characteristics and conditions for selective growth of each bacterial strain had been ascertained. After conjugations on filters had been completed, the putative transconjugants were grown in media containing antibiotics and assessed for the presence of aacC1 gene by: (a) DNA plasmid profile; (b) expression of AAC(3)-I enzyme activity; (c) colony hybridization using a ³²P-labelled DNA probe complementary to the aacC1 gene. The results obtained indicate that transfer of the aacC1 gene from genetically modified strains of R. leguminosarum into a plasmid-free strain of A. tumefaciens occurred via self-transmissible plasmids. Alternatively, genetically modified A. tumefaciens bearing the aacC1 gene on plasmids acquired from R. leguminosarum strains, transferred it ineffectively to a hardly detectable frequency. No transfer of the aacC1 gene from genetically modified R. leguminosarum or A. tumefaciens strains into P. syringae has been observed. These data indicate that in the absence of the RP4 element, genetically modified A. tumefaciens is not able to efficiently transfer aacC1 into w.t. R. leguminosarum and P. syringae. Correspondence to: A. S. Tsiftsoglou     

Expression of a foreign gene in electroporated pollen grains of tobacco

Summary The incorporation of genetically engineered DNA into pollen and subsequent fertilization of eggs by the transformed pollen would be a convenient method for producing genetically engineered seed. This method of pollen transformation would circumvent the need for other types of gene transfer methods such as the use of Agrobacterium tumefaciens, which has a limited host range and thus a limited capability for genetically engineering plants. It would also avoid the problems associated with the regeneration of some plants from tissue, cell, or protoplast culture after receiving foreign DNA. To this end, the genetically engineered plasmid DNA vector pBI221 containing the gene encoding -glucuronidase (GUS) was introduced by electroporation into germinating pollen grains of tobacco (Nicotiana gossei L.). Transient expression of the GUS gene was demonstrated by the presence of GUS activity in fluorometric assays of pollen extracts 24 h after the introduction of pBI221 via electroporation. Intact pBI221 was detected by Southern blotting procedures as a distinct DNA band in pollen extracts 1 h after electroporation. In addition, pBI221 was detected as a diffuse band of higher molecular weight DNA 24 h after electroporation, suggesting that some of the pBI221 was incorporated into the genome of the pollen.     

Luminescence-Based Systems for Detection of Bacteria in the Environment

Abstract

The development of techniques for detection and tracking of microorganisms in natural environments has been accelerated by the requirement for assessment of the risks associated with environmental release of genetically engineered microbial inocula. Molecular marker systems are particularly appropriate for such studies and luminescence-based markers have the broadest range of applications, involving the introduction of prokaryotic (lux) or eukaryotic (luc) genes for the enzyme luciferase.

Lux or luc genes can be detected on the basis of unique DNA sequences by gene probing and PCR amplification, but the major advantage of luminescence-based systems is the ability to detect light emitted by marked organisms or by luciferase activity in cell-free extracts. Luminescent colonies can be detected by eye, providing distinction from colonies of indigenous organisms, and the sensitivity of plate counting can be increased greatly by CCD imaging. Single cells or microcolonies of luminescent organisms can also be detected in environmental samples by CCD image-enhanced microscopy, facilitating study of their spatial distribution. The metabolic activity of luminescence-marked populations can be quantified by luminometry and does not require extraction of cells or laboratory growth. Metabolic activity, and potential activity, of marked organisms therefore can be measured during colonization of soil particles and plant material in real time without disturbing the colonization process.

In comparison with traditional activity techniques, luminometry provides significant increases in sensitivity, accuracy, and, most importantly, selectivity, as activity can be measured in the presence of indigenous microbial communities. The sensitivity, speed, and convenience of luminescence measurements make this a powerful technique that is being applied to the study of an increasingly wide range of ecological problems. These include microbial survival and recovery, microbial predation, plant pathogenicity, phylloplane and rhizosphere colonization and reporting of gene expression in environmental samples.     

Expression of the Bacillus thuringiensis Mosquitocidal Toxin Cry11Aa in the Aquatic Bacterium Asticcacaulis excentricus

A mosquitocidal aquatic bacterium has been developed by introducing an operon containing the cry11Aa, and p20 genes from Bacillus thuringiensis subsp. israelensis (Bti) into the gram-negative aquatic bacterium Asticcacaulis excentricus. After transformation, the cry11Aa gene was successfully expressed in recombinant A. excentricus under the tac promoter, at the level of 0.04 pg/cell. The recombinant bacteria were toxic to Aedes aegypti larvae with an LC₅₀ of 6.83 × 10⁵ cells/mL. We believe that these bacteria may have potential as genetically engineered microorganisms for the control of mosquito larvae.     

Genetically Engineered Erwinia carotovora: Survival, Intraspecific Competition, and Effects upon Selected Bacterial Genera

Environmental use of genetically engineered microorganisms has raised concerns about potential ecological impact. This research evaluated the survival, competitiveness, and effects upon selected bacterial genera of wild-type and genetically engineered Erwinia carotovora subsp. carotovora to ascertain if differences between the wild-type and genetically engineered strains exist in soil microcosms. The engineered strain contained a chromosomally inserted gene for kanamycin resistance. No significant differences in survival in nonsterile soil over 2 months or in the competitiveness of either strain were observed when the strains were added concurrently to microcosms. For reasons that remain unclear, the engineered strain did survive longer in sterilized soil. The effects of both strains on total bacteria, Pseudomonas and Staphylococcus strains, and actinomycetes were observed. While some apparent differences were observed, they were not statistically significant. A better understanding of the microbial ecology of engineered bacteria, especially pathogens genetically altered for use as biological control agents, is essential before commercial applications can be accomplished.     

基因工程微生物的环境监测及生物防御体系研究进展

随着生物技术的发展, 研究人员构建出了大量具有特定功能的基因工程微生物, 这些基因工程微生物在实际应用时常受到限制, 因为它们释放到环境中有可能带来新的污染。为了减少或消除其对环境的潜在危害, 有必要采取措施对这些基因工程微生物进行监测和安全控制。通常要求这类基因工程微生物带有便于监测的检测标记以及能进行自消亡的主动生物防御体系。对基因工程微生物的检测标记以及主动生物防御体系的研究现状进行了综述。     

基因工程微生物的环境监测及生物防御体系研究进展

随着生物技术的发展, 研究人员构建出了大量具有特定功能的基因工程微生物, 这些基因工程微生物在实际应用时常受到限制, 因为它们释放到环境中有可能带来新的污染。为了减少或消除其对环境的潜在危害, 有必要采取措施对这些基因工程微生物进行监测和安全控制。通常要求这类基因工程微生物带有便于监测的检测标记以及能进行自消亡的主动生物防御体系。对基因工程微生物的检测标记以及主动生物防御体系的研究现状进行了综述。     

Detection of foodborne pathogens using DNA probes and a dipstick format

The detection of foodborne microorganisms has traditionally been done using microbiologically based methods. Such “gold standard” methods are generally reliable but have the disadvantages of being labor intensive, subjective, and time consuming. Over the last several years, the development of DNA probe-based methods has simplified the methods used to detect organisms such asSalmonella, Listeria, andE. coli by targeting the unique DNA or RNA sequences of these organisms using DNA probes and nonradioactive detection.