| Literature DB >> 23059723 |
Indun Dewi Puspita1, Yoichi Kamagata, Michiko Tanaka, Kozo Asano, Cindy H Nakatsu.
Abstract
Many strategies have been used to increase the number of bacterial cells that can be grown from environmental samples but cultivation efficiency remains a challenge for microbial ecologists. The difficulty of cultivating a fraction of bacteria in environmental samples can be classified into two non-exclusive categories. Bacterial taxa with no cultivated representatives for which appropriate laboratory conditions necessary for growth are yet to be identified. The other class is cells in a non-dividing state (also known as dormant or viable but not culturable cells) that require the removal or addition of certain factors to re-initiate growth. A number of strategies, from simple to high throughput techniques, are reviewed that have been used to increase the cultivation efficiency of environmental samples. Some of the underlying mechanisms that contribute to the success of these cultivation strategies are described. Overall this review emphasizes the need of researchers to first understand the factors that are hindering cultivation to identify the best strategies to improve cultivation efficiency.Entities:
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Year: 2012 PMID: 23059723 PMCID: PMC4103542 DOI: 10.1264/jsme2.me12092
Source DB: PubMed Journal: Microbes Environ ISSN: 1342-6311 Impact factor: 2.912
Fig. 1Summarized concepts of typical physiological states of cells. Cells fluctuate between the states of active growth and no growth because of a number of factors that can cause inactivation and resuscitation. Cells from both these states can contribute to the fraction of uncultivable cells in laboratory experiments.
Fig. 2Cultivation strategies used to grow yet-to-be cultivated and non-dividing cells. A fraction of cells collected from natural habitats when transferred to the laboratory can be readily cultivated. In their natural habitat the cells may have been actively growing or in a non-growing state (Fig. 1). The fraction of cells that are uncultivated are categorized in this review as, yet-to-be cultivated and non-dividing cells.
The cultivation efficiency of cells from various environmental samples
| Habitat | Cultivation efficiency | Media for cultivation | Method for direct counts | Reference |
|---|---|---|---|---|
| Desert | 0.0007–0.02 | R2A | PLFA | ( |
| 0.02–0.15 | R2A | PLFA | ( | |
| 0.05–0.1 | TSA | PLFA | ( | |
| Permafrost sediment | 0.001–10 | Poor and rich media | AO | ( |
| 0.03 | R2A | SYTO9/PI | ( | |
| Heavy metal-contaminated soil | 0.08–2.27 | R2A | DTAF | ( |
| 0.03–1.48 | TSBA | DTAF | ( | |
| Soil | 2.4–19 | VL55 | DAPI, AO | ( |
| Marine sediment | 2.5M | ABW | DAPI | ( |
| Sea water | 0.25M | ABW | DAPI | ( |
| 0.003 | Marine R2A | DAPI | ( | |
| 0.01–0.98 | 1/10 Marine R2A | DAPI | ( | |
| 0.01–0.15 | Marine R2A | DAPI | ( | |
| Lake sediment | 0.1 | PE03-7A | EtBr | ( |
| 1.3 | PE03-7G | EtBr | ( | |
| 0.007–0.017 | ABM | SYTO9/PI | ( | |
| Fresh water | 0.1–5.59M | Synthetic fresh water | DAPI | ( |
| Activated sludge | 13.86 | LB agar | DAPI | ( |
| 0.24–0.38 | TSA | DAPI | ( | |
| 1.67–3.68 | R2A | DAPI | ( | |
| Human feces | 54 | Medium 10 | DAPI | ( |
| 14.28 | BBA | DAPI | ( | |
| 36.5 | BBA | DAPI | ( | |
| 58 | Medium 10 | n.r. | ( |
Cultivation efficiency was calculated from the percentage of cultivable cells from colony forming units or MPN countsM in proportion to total number of live cells from direct counts.
Cultivation was performed aerobically except for human feces that were grown anaerobically.
Direct counts were made microscopically after staining with AO (Acridine orange), DAPI (4′,6-diamidino-2-phenylindole), DTAF (5-(4,6-dichlorotriazin-2-yl)aminofluorescein), ethidium bromide (EtBr) or SYTO9/PI (SYTO9 and propidium iodide) except for estimations made from phospholipid fatty acid (PLFA) analysis.
not reported
Characteristics of non-dividing cellsa of non-spore forming bacteria
| Parameters | Characteristics | References |
|---|---|---|
| Cell size | Size reduction | ( |
| Cell morphology | Change in cell shape ( | ( |
| Cell membrane phospholipid | Reduction of phosphatidylglycerol, increase of cardiolipin content, and increase in saturated fatty acid | ( |
| Electrochemical properties | Increase of particle conductivity (due to thickening of cell wall) and decrease of electrochemical activities | ( |
| Ribosome | Reduction of ribosomes | ( |
| DNA | Poorly visible nucleoid but DNA still present | ( |
| Metabolic activity | Reduction of metabolic activity, membrane oxydase activity, and dehydrogenase activity | ( |
| Total cell protein | Reduction of cytoplasmic protein | ( |
| Fatty acid | Reduction of fatty acid content and change in lipid composition | ( |
Characteristics differences are in respect to actively growing cells of non-spore forming bacteria.
Compounds used to resuscitate non-dividing cells of several non-spore forming bacteria induced in the laboratory.
| Compounds | Microorganism | Method used to induce cells into non dividing state | References |
|---|---|---|---|
| H2O2 degrading compound | Starvation, low temperature | ( | |
| Starvation, low temperature | ( | ||
| Starvation, low temperature | ( | ||
| Starvation, low temperature | ( | ||
| Starvation, low temperature | ( | ||
| Starvation, low temperature | ( | ||
| Starvation, low temperature | ( | ||
| Rpf | Starvation | ( | |
| Starvation, hypoxic | ( | ||
| Starvation | ( | ||
| Starvation | ( | ||
| Starvation | ( | ||
| Lipid | Starvation | ( | |
| Peptide | Starvation | ( | |
| YeaZ protein | Osmotic stress | ( |
resuscitation promoting factor
Compounds tested to increase cell numbers grown from environmental samples collected from various habitats
| Compounds | Habitat | Specific taxa reported | Reference |
|---|---|---|---|
| cAMP | Sea water and sediment | Strain G100, New Rhodobacteraceae | ( |
| Eutrophic lake | Two new Actinomycetales | ( | |
| AHL | Sea water and sediment | No specific taxa reported | ( |
| Peptidoglycans | Estuarine water | No specific taxa reported | ( |
| Peptide | Intertidal sand sediment | ( | |
| Siderophore | Intertidal sand sediment | ( | |
Specific taxa noted by authors that apparently depended on the presence of the added compound for growth in laboratory culture medium. In most cases taxa names were for most closely related identified species but more in-depth identification may demonstrate that these taxa represent new genera.
cyclic adenosine monophosphate
N-acyl homoserine lactone