Microcosm for assessing survival of genetically engineered microorganisms in aquatic environments

Laboratory-contained microcosms are important for studying the fate and survival of genetically engineered microorganisms. In this study, we describe a simple aquatic microcosm that utilizes survival chambers in a flowthrough or static renewal system. The model was used to study the survival of genetically engineered and wild-type strains of Escherichia coli and Pseudomonas putida in the lake water environment. Temperature-dependent studies indicated that the genetically engineered microorganisms survived better or at least as well as their wild-type counterparts at 15, 25, and 30 degrees C. The genetic determinants of the genetically engineered microorganisms also remained fairly stable within the host cell under the tested conditions. In the presence of organisms indigenous to lake water, E. coli was eliminated after 20 days, whereas P. putida showed an initial decline but was able to stabilize its population after 5 days. A herbicide, Hydrothol-191, caused a significant decline in numbers of P. putida, but no significant difference was observed between the genetically engineered microorganisms and the wild-type strain. The microcosm described is simple, can be easily adapted to study a variety of environmental variables, and has the advantage that the organisms tested are constantly exposed to test waters that are continuously renewed.     

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 ~ -1.00 day^?1), then moderately after 5 to 28 days (-0.10~, -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-µm 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.     

Autecological properties of 3-chlorobenzoate-degrading bacteria and their population dynamics when introduced into sediments

Ecologically significant properties of wild-type and genetically engineered bacteria capable of degrading 3-chlorobenzoate (3-CB) were compared in the laboratory, and isolates were introduced into streambed sediments in microcosms to observe their population dynamics. 3-CB metabolism, growth on algal extract, temperature optima, and ingestion by protozoa were ecological properties considered relevant to the persistence of these bacteria if introduced into nature. Cell-specific Vmax for 3-CB metabolism and cell-specific mineralization rates each spanned approximately 2 orders of magnitude, but isolates did not rank consistently. The Ks for 3-CB metabolism for Alcaligenes sp. BR60 was approximately 40-fold lower than the mean value for the other isolates, which differed only approximately 4-fold among themselves. All isolates grew on an algal extract nearly as well as on tryptone-yeast extract, implying potential for survival on natural metabolic substrates in situ. Most isolates had temperature optima that were 3-15 degrees C higher than maximum stream water temperature (22 degrees C). Ciliates preferentially ingested P. acidovorans M3GY, and either P. putida RC-4(pSI30) or its parent strain were least preferred, but microflagellates did not exhibit consistent preferences. Fluorescent antibodies were prepared against isolates to permit detection of target cells in natural communities. In three different microcosm experiments the cell densities of introduced isolates declined over a period of days. In one experiment, 3-CB additions (100 mg/L) led to increases of P. alcaligenes C-0 and P. acidovorans M3GY cell densities within 1 day, although P. putida RC-4(pSI30) took 4 days. In a second experiment, the persistence of P. putida RC-4(pSI30) and its parent strain P. putida RC-4 were compared and rates of initial population decline were not statistically different. 3-CB addition stimulated the growth of other organisms while densities of the P. putida strains further declined. In a third experiment exposure to 100 mg 3-CB/L slowed the rate of decline of P. acidovorans M3GY densities compared to a 10 mg/L concentration or unamended control. Competition with the native flora was a significant factor affecting the persistence of introduced 3-CB degraders.     

The Incorporation of Farnesol-2-14C into Ipomeamarone

The survival of genetically engineered and wild-type Pseudomonas putida PpY101, that contained a recombinant plasmid pSR134 conferring mercury resistance, were monitored in andosol and sand microcosms. The survival of genetically engineered and wild-type P. putida was not significantly different in andosol. The population change of the two strains was dissimilar in andosol and sand. The survival of genetically engineered and wild-type P. putida strains was affected by the water content of andosol, and increased with the increment of the water content. The impact of the addition of genetically engineered and wild-type P. putida strains on indigenous bacteria and fungi was examined. Inoculation of both strains had no apparent effect on the density of indigenous microorganisms.     

Survival and detection of bacteria in an aquatic environment.

A genetically engineered plasmid, pPSA131, was used as a DNA probe to detect homologous DNA in Escherichia coli HB101(pPSA131) after it was mixed with aquatic microorganisms from Lake Mead, Nevada, water samples. An isolate from the pLAFR1 chromosomal library of Pseudomonas syringae Cit 7 was used to detect parent P. syringae Cit 7 that had been mixed with Lake Mead water. E. coli(pPSA131) was kept in variously treated samples of lake water or buffer, and its survival was measured by viable cell counting on modified Luria-Bertani (LB) agar. Full-strength LB agar proved better than 0.1 x LB agar at recovering E. coli(pPSA131) after survival in low-nutrient environments. Survival of E. coli(pPSA131) remained high in filtered (0.22-micron pore size) lake water and salts buffer on both selective and nonselective agars but was lower in untreated lake water or lake water filtered with a 0.8-micron-pore-size membrane. Total recoverable colonies grown on LB agar were higher when lake water was filter treated (0.8-micron pore size) than when lake water was untreated. Microorganisms recovered from lake water alone grew rapidly on nonselective media, probably because of the "bottle effect." After being mixed with Lake Mead water, E. coli(pPSA131) and P. syringae were detected by colony blotting with non-radioactively labeled DNA probes. E. coli(pPSA131) were recovered at three times during 48 h from variously treated samples of lake water and from a mixture with Lake Mead water organisms. Colonies were supported on either nonselective or selective agar for comparison.(ABSTRACT TRUNCATED AT 250 WORDS)     

Survival and detection of bacteria in an aquatic environment

A genetically engineered plasmid, pPSA131, was used as a DNA probe to detect homologous DNA in Escherichia coli HB101(pPSA131) after it was mixed with aquatic microorganisms from Lake Mead, Nevada, water samples. An isolate from the pLAFR1 chromosomal library of Pseudomonas syringae Cit 7 was used to detect parent P. syringae Cit 7 that had been mixed with Lake Mead water. E. coli(pPSA131) was kept in variously treated samples of lake water or buffer, and its survival was measured by viable cell counting on modified Luria-Bertani (LB) agar. Full-strength LB agar proved better than 0.1 x LB agar at recovering E. coli(pPSA131) after survival in low-nutrient environments. Survival of E. coli(pPSA131) remained high in filtered (0.22-micron pore size) lake water and salts buffer on both selective and nonselective agars but was lower in untreated lake water or lake water filtered with a 0.8-micron-pore-size membrane. Total recoverable colonies grown on LB agar were higher when lake water was filter treated (0.8-micron pore size) than when lake water was untreated. Microorganisms recovered from lake water alone grew rapidly on nonselective media, probably because of the "bottle effect." After being mixed with Lake Mead water, E. coli(pPSA131) and P. syringae were detected by colony blotting with non-radioactively labeled DNA probes. E. coli(pPSA131) were recovered at three times during 48 h from variously treated samples of lake water and from a mixture with Lake Mead water organisms. Colonies were supported on either nonselective or selective agar for comparison.(ABSTRACT TRUNCATED AT 250 WORDS)     

Monitoring genetically engineered microorganisms in freshwater microcosms

Summary The effectiveness of gene probe methods for tracking genetically engineered microorganisms (GEMs) in the environment was tested by inoculating nutrient-supplemented freshwater microcosms withAlcaligenes A5 (a naturally occurring 4-chlorobiphenyl degrader) orPseudomonas cepacia AC1100 (a genetically engineered 2, 4, 5 T-degrader) and following the fates of the introduced bacterial populations. Colony hybridization of the viable heterotrophic bacterial populations and dot blot hybridization of DNA recovered from the total microcosm microbial communities showed persistence of bothAlcaligenes A5 andP. cepacia AC1100 in the microcosms in the presence and absence of the xenobiotic substrates that these organisms biodegrade. Although there was a gradual decline in the added populations, both of the bacterial populatins were still detected in the microcosms two months after their introduction into the microcosms. Addition of 2, 4, 5-T enhanced the survival ofP. cepacia AC1100 — and 4-chlorobiphenyl addition resulted in increased levels ofAlcaligenes A5. The results indicate that both organisms may persist for very long periods in freshwater habitats.     

Tracking genetically engineered bacteria: monoclonal antibodies against surface determinants of the soil bacterium Pseudomonas putida 2440.

Assessment of potential risks involved in the release of genetically engineered microorganisms is facilitated by the availability of monoclonal antibodies (MAbs), a tool potentially able to monitor specific organisms. We raised a bank of MAbs against the soil bacterium Pseudomonas putida 2440, which is a host for modified TOL plasmids and other recombinant plasmids. Three MAbs, 7.3B, 7.4D, and 7.5D, were highly specific and recognized only P. putida bacteria. Furthermore, we developed a semiquantitative dot blot assay that allowed us to detect as few as 100 cells per spot. A 40-kDa cell surface protein was the target for MAbs 7.4D and 7.5D. Detection of the cell antigen depended on the bacterial growth phase and culture medium. The O antigen of lipopolysaccharide seems to be the target for MAb 7.3B, and its in vivo detection was independent of the bacterial growth phase and culture medium. MAb 7.3B was used successfully to track P. putida (pWW0) released in unsterile lake mesocosms.     

Improved phosphate biosorption by bacterial surface display of phosphate-binding protein utilizing ice nucleation protein

The conventional enhanced biological phosphorus removal (EBPR) system often deteriorates at low chemical oxygen demand (COD) or under aeration conditions. A new approach that incorporates phosphate-eutrophic wastewater remediation was introduced through immobilization of an intracellular phosphate-binding protein (PBP) onto the surface of Pseudomonas putida or Escherichia coli , using the N-terminal anchor (InaQ-N) of a newly identified ice nucleation protein from Pseudomonas syringae . A green fluorescent protein-fusion protein was expressed and used to confirm surface localization. The PBP was then targeted to the surface of E. coli JM109 and P. putida AB92019. The engineered P. putida and E. coli microorganisms were capable of absolute biosorption of total phosphates at rates of 60 and 80 mg L⁻¹, respectively, over 5 h. In the recombinant P. putida cells, a surface-immobilized PBP fusion that had three tandemly repeated InaQ-Ns exhibited the maximum increment in phosphate biosorption, at sixfold compared with the control strain. Even heat-killed recombinant cells of either P. putida or E. coli retained substantial biosorptive activities. The current study demonstrates that the bacterial surface display of PBP should be considered as a strong contender for generating organisms capable of functioning in EBPR systems under low COD, resulting in improved removal of eutrophic phosphorus from wastewaters.     

Survival of bacteria during aerosolization

One form of commercial application of microorganisms, including genetically engineered microorganisms is as an aerosol. To study the effect of aerosol-induced stress on bacterial survival, nonrecombinant spontaneous antibiotic-resistant mutants of four organisms, Enterobacter cloacae, Erwinia herbicola, Klebsiella planticola, and Pseudomonas syringae, were sprayed in separate experiments in a greenhouse. Samples were collected over a distance of 15 m from the spray site for enumeration. Spores of Bacillus subtilis were used as tracers to estimate the effects of dilution on changes in population over distance. Viable counts of P. syringae, Enterobacter cloacae, and K. planticola decreased significantly over a distance of 15 m. Erwinia herbicola showed no significant decline in counts over the same distance. The degree of survival of P. syringae during aerosolization was dependent on ambient environmental conditions (i.e., temperature, relative humidity), droplet size of the aerosol, and prior preparative conditions. Survival was greatest at high relative humidities (70 to 80%) and low temperatures (12 degrees C). Survival was reduced when small droplet sizes were used. The process of washing the cells prior to aerosolization also caused a reduction in their survival. Results from these experiments will be useful in developing sound methodologies to optimize enumeration and for predicting the downwind dispersal of airborne microorganisms, including genetically engineered microorganisms.     

Survival of bacteria during aerosolization.

One form of commercial application of microorganisms, including genetically engineered microorganisms is as an aerosol. To study the effect of aerosol-induced stress on bacterial survival, nonrecombinant spontaneous antibiotic-resistant mutants of four organisms, Enterobacter cloacae, Erwinia herbicola, Klebsiella planticola, and Pseudomonas syringae, were sprayed in separate experiments in a greenhouse. Samples were collected over a distance of 15 m from the spray site for enumeration. Spores of Bacillus subtilis were used as tracers to estimate the effects of dilution on changes in population over distance. Viable counts of P. syringae, Enterobacter cloacae, and K. planticola decreased significantly over a distance of 15 m. Erwinia herbicola showed no significant decline in counts over the same distance. The degree of survival of P. syringae during aerosolization was dependent on ambient environmental conditions (i.e., temperature, relative humidity), droplet size of the aerosol, and prior preparative conditions. Survival was greatest at high relative humidities (70 to 80%) and low temperatures (12 degrees C). Survival was reduced when small droplet sizes were used. The process of washing the cells prior to aerosolization also caused a reduction in their survival. Results from these experiments will be useful in developing sound methodologies to optimize enumeration and for predicting the downwind dispersal of airborne microorganisms, including genetically engineered microorganisms.     

Construction of a stable genetically engineered rhamnolipid-producing microorganism for remediation of pyrene-contaminated soil

One rhamnolipid-producing bacterial strain named Pseudomonas aeruginosa BSFD5 was isolated and characterized. Its rhlABRI cassette including necessary genes for rhamnolipid synthesis was cloned and transformed into the chromosome of P. putida KT2440 by a new random transposon vector without introducing antibiotic-resistance marker, generating a genetically engineered microorganism named P. putida KT2440-rhlABRI, which could stably express the rhlABRI cassette and produce rhamnolipid at a yield of 1.68?g?l(-1). In experiments using natural soil, it was shown that P. putida KT2440-rhlABRI could increase the dissolution of pyrene and thus promote its degradation by indigenous microorganisms. P. putida KT2440-rhlABRI thus demonstrated potential for enhancing the remediation of soils contaminated with polycyclic aromatic hydrocarbons.     

Use of green fluorescent protein to monitor survival of genetically engineered bacteria in aquatic environments.

Many methods for detecting model genetically engineered microorganisms (GEMs) in experimental ecosystems rely on cultivation of introduced cells. In this study, survival of Escherichia coli was monitored with the green fluorescent protein (GFP) gene. This approach allowed enumeration of GEMs by both plating and microscopy. Use of the GFP-marked GEMs revealed that E. coli persisted in stream water at higher densities as determined microscopically than as determined by CFU enumeration. The GFP gene did not negatively impact the fitness of the host strain.     

Novel method for monitoring genetically engineered microorganisms in the environment.

A method has been devised for directly detecting and monitoring genetically engineered microorganisms (GEMs) by using in vitro amplification of the target DNAs by a polymerase chain reaction and then hybridizing the DNAs with a specific oligonucleotide or DNA probe. A cloned 0.3-kilobase napier grass (Pennisetum purpureum) genomic DNA that did not hybridize to DNAs isolated from various microorganisms, soil sediments, and aquatic environments was inserted into a derivative of a 2,4-dichlorophenoxyacetic acid-degradative plasmid, pRC10, and transferred into Escherichia coli. This genetically altered microorganism, seeded into filter-sterilized lake and sewage water samples (10(4)/ml), was detected by a plate count method in decreasing numbers for 6 and 10 days of sample incubation, respectively. The new method detected the amplified unique marker (0.3-kilobase DNA) of the GEM even after 10 to 14 days of incubation. This method is highly sensitive (it requires only picogram amounts of DNA) and has an advantage over the plate count technique, which can detect only culturable microorganisms. The method may be useful for monitoring GEMs in complex environments, where discrimination between GEMs and indigenous microorganisms is either difficult or requires time-consuming tests.     

A DNA module encoding bph genes for the degradation of polychlorinated biphenyls (PCBs)

Abstract In this report we describe the development and construction of a DNA module which encodes bph genes for the metabolism of PCBs and which is capable of stable integration into the chromosome of Gram negative bacteria. Introduction of the bph -module into Pseudomonas putida KT2442, Pseudomonas sp. strain B13 and its genetically engineered derivative B13FR1 expanded the biodegradative ability of these strains to include biphenyl and 4-chlorobiphenyl. The bph operon was stably inherited under laboratory conditions. Behavior of the genetically engineered strains was evaluated under simulated natural habitat conditions in lake sediment microcosms with respect to survival and removal of 4-chlorobiphenyl. The genetically engineered strains persisted under these conditions and were effective in degrading 4-chlorobiphenyl over a five day incubation period.     

Genetically Engineered Erwinia carotovora in Aquatic Microcosms: Survival and Effects on Functional Groups of Indigenous Bacteria

The survival of genetically engineered Erwinia carotovora L-864, with a kanamycin resistance gene inserted in its chromosome, was monitored in the water and sediment of aquatic microcosms. The density of genetically engineered and wild-type E. carotovora strains declined at the same rate, falling in 32 days below the level of detection by viable counts. We examined the impact of the addition of genetically engineered and wild-type strains on indigenous bacteria belonging to specific functional groups important in nutrient cycling. For up to 16 days, the densities of total and proteolytic bacteria were significantly higher (P < 0.05) in microcosms inoculated with genetically engineered or wild-type E. carotovora, but by 32 days after inoculation, they had decreased to densities similar to those in control microcosms. Inoculation of genetically engineered or wild-type E. carotovora had no apparent effect on the density of amylolytic and pectolytic bacteria in water and sediment. Genetically engineered and wild-type E. carotovora did not have significantly different effects on the densities of specific functional groups of indigenous bacteria (P > 0.05).     

Adaptation of model genetically engineered microorganisms to lake water: growth rate enhancements and plasmid loss.

When a genetically engineered microorganism (GEM) is released into a natural ecosystem, its survival, and hence its potential environmental impact, depends on its genetic stability and potential for growth under highly oligotrophic conditions. In this study, we compared plasmid stability and potential for growth on low concentrations of organic nutrients of strains of Pseudomonas putida serving as model GEMs. Plasmid-free and plasmid-bearing (NAH7) prototrophic isogenic strains and two amino-acid auxotrophs, all containing antibiotic resistance markers, were held physically separate from but in chemical contact with lake water containing the natural bacterium-sized microbial populations. Cells were reisolated at intervals over a 2-month period to determine the percent retaining the plasmid and the specific growth rate on various media. Plasmid stability in lake water was strongly strain specific; the NAH7 plasmid was stably maintained by the prototrophic strain for the duration of the test but was lost within 24 h by both of the auxotrophs. Specific growth rates of reisolates, compared with those of the corresponding non-lake water-exposed strains (i.e., parental strains), were not different when measured in rich medium (Luria-Bertani broth). However, specific growth rates were 42, 55, and 63% higher in reisolates of auxotrophs and the plasmid-free prototroph, respectively, when measured in 10-fold-diluted medium after exposure of 15 days or longer to lake water. Moreover, lake water-exposed strains grew actively when reintroduced into sterile lake water (28- to 33-fold increase in numbers over 7 days), while the corresponding unadapted parental strains exhibited no growth over the same period.(ABSTRACT TRUNCATED AT 250 WORDS)     

Biodegradation of phenoxyacetic acid in soil by Pseudomonas putida PP0301(pR0103), a constitutive degrader of 2, 4–dichlorophenoxyacetate

The efficacy of using genetically engineered microbes (GEMs) to degrade recalcitrant environmental toxicants was demonstrated by the application of Pseudomonas putida PP0301(pR0103) to an Oregon agricultural soil amended with 500 micrograms/g of a model xenobiotic, phenoxyacetic acid (PAA). P. putida PP0301(pR0103) is a constitutive degrader of 2,4-dichlorophenoxyacetate (2,4-D) and is also active on the non-inducing substrate, PAA. PAA is the parental compound of 2,4-dichlorophenoxyacetic acid (2,4-D) and whilst the indigenous soil microbiota degraded 500 micrograms/g 2,4-D to less than 10 micrograms/g, PAA degradation was insignificant during a 40-day period. No significant degradation of PAA occurred in soil inoculated with the parental strain P. putida PP0301 or the inducible 2,4-D degrader P. putida PP0301(pR0101). Moreover, co-amendment of soil with 2,4-D and PAA induced the microbiota to degrade 2,4-D; PAA was not degraded. P. putida PP0301-(pR0103) mineralized 500-micrograms/g PAA to trace levels within 13 days and relieved phytotoxicity of PAA to Raphanus sativus (radish) seeds with 100% germination in the presence of the GEM and 7% germination in its absence. In unamended soil, survival of the plasmid-free parental strain P. putida PP0301 was similar to the survival of the GEM strain P. putida PP0301(pR0103). However, in PAA amended soil, survival of the parent strain was over 10,000-fold lower (< 3 colony forming units per gram of soil) than survival of the GEM strain after 39 days.     

Adaptation of model genetically engineered microorganisms to lake water: growth rate enhancements and plasmid loss.

When a genetically engineered microorganism (GEM) is released into a natural ecosystem, its survival, and hence its potential environmental impact, depends on its genetic stability and potential for growth under highly oligotrophic conditions. In this study, we compared plasmid stability and potential for growth on low concentrations of organic nutrients of strains of Pseudomonas putida serving as model GEMs. Plasmid-free and plasmid-bearing (NAH7) prototrophic isogenic strains and two amino-acid auxotrophs, all containing antibiotic resistance markers, were held physically separate from but in chemical contact with lake water containing the natural bacterium-sized microbial populations. Cells were reisolated at intervals over a 2-month period to determine the percent retaining the plasmid and the specific growth rate on various media. Plasmid stability in lake water was strongly strain specific; the NAH7 plasmid was stably maintained by the prototrophic strain for the duration of the test but was lost within 24 h by both of the auxotrophs. Specific growth rates of reisolates, compared with those of the corresponding non-lake water-exposed strains (i.e., parental strains), were not different when measured in rich medium (Luria-Bertani broth). However, specific growth rates were 42, 55, and 63% higher in reisolates of auxotrophs and the plasmid-free prototroph, respectively, when measured in 10-fold-diluted medium after exposure of 15 days or longer to lake water. Moreover, lake water-exposed strains grew actively when reintroduced into sterile lake water (28- to 33-fold increase in numbers over 7 days), while the corresponding unadapted parental strains exhibited no growth over the same period.(ABSTRACT TRUNCATED AT 250 WORDS)     

Genetic analysis of an incomplete mutS gene from Pseudomonas putida

We genetically characterized the Pseudomonas putida mutS gene and found that it encodes a smaller MutS protein than do the genes of other bacteria. This gene is able to function in the mutS mutants of Escherichia coli and Bacillus subtilis. A P. putida mutS mutant has a mutation frequency 1,000-fold greater than that of the wild-type strain.