image © Phage et al. Bacteriophage Ecology Group (BEG) News
Dedicated to the ecology and evolutionary biology of the parasites of unicellular organisms (UOPs)
© Stephen T. Abedon (editor)
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© Phage et al. January 1, 2002 issue (volume 11)

At this site you will find . . .

1. editorial this page
2. new BEG members this page
3. new links this page
4. new features this page
5. meetings this page
6. jobs this page
7. submissions (a.k.a., stuff to read) this page
8. letters this page
9. phage image this page
10. new publications (abstracts) this page
11. acknowledgements this page
12. Bacteriophage Ecology Group elsewhere
13. comments mail to

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Editorial

Editorials should be written on subjects relevant to The Bacteriophage Ecology Group as an organization, to BEG News (either the concept or a given issue of BEG News), or the science of Bacteriophage Ecology. While my assumption is that I will be writing the bulk of these editorials, I wish to encourage as many people as possible to seek to relieve me of this duty, as often as possible. Additionally, I welcome suggestions of topics that may be addressed. Please address all correspondences to abedon.1@osu.edu or to "Editorials," Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. Please send all submissions as Microsoft Word documents, if possible (I'll let you know if I have trouble converting other document formats), and in English.

Mathematics for Microbiologists

The evolution of the Latin alphabet

Microbiologists are not a terribly mathematically inclined bunch. If we were, we probably wouldn't be microbiologists. Indeed, microbiology is difficult enough without introducing math into one's research equation. Nevertheless, for complex systems mathematical analysis can be simplifying, at least in terms of the synthesis of multiple ideas and data, and, ideally, can even be predictive! This is particularly so for microbial ecology, where one must worry about population-level effects on top of biochemical, morphological, physiological, and genetical complexity. So, consequently, we're stuck with math. Does that mean that microbiology that's mathematically based must be completely opaque to the non-mathematician? Nooooo! Here, then, is a cued guide for the mathematically oriented on how to bring one's math down to a level that a mere microbiologist might understand:

Microbiology: Keep the microbiology in the fore, not the math.
Continuity: Strive for continuity with previous mathematical analyses of the same or similar phenomena.
Latin: When starting analyses from scratch, try to avoid assigning Greek letters as variable names; e.g., to the not Greek or not mathematically inclined, B is preferable to b.
Expansion: Outside of equations don't use variable names as abbreviations for phenomena; e.g., don't write simply B if what your really mean is burst size.
Redundance: Strive for redundancy by redefining your variables throughout your text.
Comprehension: Assume minimal mathematical knowledge among your readers. Don't omit crucial logical steps in the development of your math. Mathematicians may scoff at excess detail, but microbiologists, in its absence, will simply become confused.
Interpretation: You are writing microbiology for microbiologists so try explaining what each equation means in microbiological terms.
Justification: Explain why you are using a particular mathematical technique, just as you should always strive to justify your utilization of an unusual experimental technique.
Supervision: In multi-authored studies, don't leave the mathematician alone to write the theory section!
Closure: Eventually return your study to the microbiology.

When written well a study that considers the mathematics of a microbiological phenomenon ultimately should lead the reader to an intuitive understanding of the phenomenon. Barring that, the reader should gain an understanding of why the phenomenon cannot be understood intuitively (usually meaning that it is either too complex or too poorly understood to be sufficiently mechanistically developed). A study that fails to develop significant biological understanding cannot lead its readers to intuitive knowledge, and chances are your more microbiologically minded colleagues will ignore it. Finally, this is a call for conscientious improvement rather than perfection. No doubt my own published math, simplistic as it is, may be criticized as insufficiently transparent for the casual reader.

MicroDude, a.k.a., Stephen T. Abedon
is the Developer and Editor of The Bacteriophage Ecology Group web site which is dedicated to the ecology and evolutionary biology of the parasites of unicellular organisms (UOPs)

Editorial Archive

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New BEG Members

The BEG members page can be found at www.phage.org/beg_members.htm. There are two ways of "joining" BEG. One, the "traditional" way, is to have your name listed on the web page and on the list server. The second, the "non-traditional" way, is to have your name only listed on the list server. The latter I refer to as "non-members" on that list. Members, e.g., individuals listed on the BEG members list page, should be limited to individuals who are actively involved in science (research, instruction, outreach, industry) and who can serve as a phage ecology resource to interested individuals. If you have an interest in phage ecology but no real expertise in the area, then you should join as a non-member. To join as a member, please contact BEG using the following link: abedon.1@osu.edu. Include:
  • your name
  • your e-mail address
  • your snail-mail address
  • the URL of your home page (if you have one)
  • a statement of whether or not you are the principal investigator
  • a statement of your research interests (or phage ecology interests)
  • a list of your phage ecology references, if any
Note that it is preferable that you include the full reference, including the abstract, if the reference is not already present in the BEG bibliography. Responsibility of members includes keeping the information listed on the BEG members page up to date including supplying on a reasonably timely basis the full references of your new phage ecology publications. Reprints can also be sent to The Bacteriophage Ecology Group, care of Stephen Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. To join BEG as a non-member, please contact BEG using the following link: abedon.1@osu.edu and minimally include your name and e-mail address.

Please welcome our newest members

name
(home page links)
status e-mail address
Faith Burden --- fburden
@bio.warwick.ac.uk
Biological Sciences Dept., University of Warwick, Coventry, UK CV4 7AL
interests:Ecology of temperate bacteriophage of Staphylococcus aureus. The use of bacteriophage therapy against MRSA. (contents | BEG members | top of page)
Lin Tao PI ltao
@uic.edu
Associate Professor, Department of Oral Biology, College of Dentistry, M/C 690, University of Illinois at Chicago, 801 S. Paulina Street, Chicago, IL 60612, USA
interests:Phage-lactobacillus interaction, lactobacillus phage taxonomy and classification, symbiosis and coevolution among women, their vaginal lactobacilli and phages, and the role of sexually transmissible phages in the health and diseases of women. (contents | BEG members | top of page)
Yanhui Yang --- yanhui
@jingxian.xmu.edu.cn
Center for Marine Environmental Studies, Xiamen University, Xiamen, 361005, P. R. China
interests:Relationship between virus and prokaryotic picoplankton in estuary, coastal zone, shelf sea and open waters. Changes in diversity and community structure of viral and picoplankton community along eco-type gradients. (contents | BEG members | top of page)

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New Links

Links relevant to The Bacteriophage Ecology Group fall into a number of categories (e.g., see Bacteriophage Ecology Links at www.phage.org/beg_links.htm). Listed below are new links found on that page. If you know of a link that should be included on this page, or the whereabouts of a now-dead link, please let me know.
No Entry.

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New Features

In this section I highlight new or updated features of the BEG site. If you have any ideas of how either the BEG site or BEG News might be improved, please let me know.
The BEG Meetings page has been updated for the 2002 year.

The look of the site has been updated. See www.phage.org (below) and enjoy!

The new BEG splash page

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Meetings

The BEG Meetings link will continue. Reminders of upcoming meetings will be placed in this section of BEG News. If you know of any meetings that might be of interest to BEG members, or would like to recap a meeting that you've attended, then please send this information for posting to abedon.1@osu.edu or to "BEG Meetings," Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906.

Please send photos, etc. from meetings for inclusion in this section.

This is a list of some of what appears to be going on in 2002:

See the BEG Meetings Page for a Calendar and a Meetings overview.
Click on links for more detail.

  1. Society of Integrative and Comparative Biology Meeting (January-annual)
  2. ASM General Meeting (May-annual)
  3. American Society for Virology Meeting (July-annual)
  4. Molecular Genetics of Bacteria & Phages (mid-August-annual)
  5. International Congress of Virology (late August-biennial?)
  6. European Marine Microbiology Symposium (October-?)

This is an initial list of what may or may not be going on in 2003:

  1. Society of Integrative and Comparative Biology Meeting (January-annual)
  2. ASM General Meeting (May-annual)
  3. American Society for Virology Meeting (July-annual)
  4. International Phage Meeting (June, July, August?-biennial, even years; now odd? now annual?)
  5. Microbial Population Biology Gordon Conference (July, August-biennial, odd years)
  6. Molecular Genetics of Bacteria & Phages (mid-August?-annual)
  7. ???International Congress of Virology (late August?-biennial?)
  8. International Society Microbial Ecology (late August?-biennial, odd years)
  9. ???European Marine Microbiology Symposium (October-?)

Below is a scene from the opening-day picnic at Evergreen, 2001
(that's MicroDude wearing the funny glasses):

Scene from the opening-day picnic at Evergreen, 2001 (that's MicroDude wearing the funny glasses)

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Jobs

Looking for job? Looking to fill a position? Please send advertisement and information to abedon.1@osu.edu or to "Jobs", Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. Please send all information as text (e.g., as an e-mail) or as Microsoft Word documents, if possible (I'll let you know if I have trouble converting any other document formats), and in English. I will update this section as I receive material, regardless of what date this issue of BEG News goes live.

Click here for International Society for Microbial Ecology Employment Listings.

Click here for American Association for the Advancement of Science Employment Listings.

Click here for AAAS "Microbial Ecology" Search.

Click here for AAAS Ecology and Microbiology.

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Submissions

Submissions are non-editorial items describing or highlighting some aspect of bacteriophage ecology including news pieces, historical pieces, reviews, and write-ups of research. Peer review of submissions is possible and a desire for peer review should be indicated. Send all submissions to abedon.1@osu.edu or to "Submissions", Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. Please send all submissions as Microsoft Word documents, if possible (I'll let you know if I have trouble converting any other document formats), and in English.

An Expanded Overview of Phage Ecology

by Stephen T. Abedon

(for a more easily printed version, click here)

[Note: Do not reference this manuscript. Instead, please see the Phage Ecology chapter by Stephen T. Abedon as it is to appear in The Bacteriophages, Edition 2, Oxford University Press. The manuscript submission deadline for that publication is February 1, 2002. This manuscript, as presented, is not in final submission form. Any comments and criticisms on this manuscript sent prior to the submission deadline would be greatly appreciated by the author. Please send by e-mail to abedon.1@osu.edu. Thanks.]

Contents

1. Introduction
2. Phage Organismal Ecology
a. The basic phage life cycle
b. Phage adsorption
c. Infection (the latent period)
d. Phage-progeny release
e. Phage decay
3. Phage Population Ecology
a. Phage latent-period evolution
b. Contribution of early adsorbers
c. Phage plaque growth
4. Phage Community Ecology
a. Community stability
b. Refuges
c. Slowed adsorption
d. Reduced phage productivity
e. Synthesis
5. Phage Ecosystem Ecology
6. References

Introduction

Phage ecology is the study of the real-time interactions between phages and environments. These interactions are ecologically important, particularly to the extent that they affect bacteria populations. Here - keeping phages in the fore rather than bacteria or ecosystem functioning - I consider phage organismal, population, community, and ecosystem ecology (Table 1). For complementary approaches to the review of phage ecology see (6,7,11,18,23,39,47,51), plus various recent reviews of aquatic and ecosystem phage ecology (38,53,57,63,64,69,73).

Table 1: Defining Phage Ecology

Ecology A bacterium is... Considerations Experiments
Organismal ...a target, or an entity that impacts on the phage phenotype Phage anatomy, physiology, and behavior characterized from Darwinian perspective; virion stability, survival, and adsorption; eclipse period, latent period, and burst size; adaptations overcoming barriers to transmission Single-step growth; adsorption curves; kinetics of phage decay
Population ...an environmental resource Phage population growth and density; liquid versus spatially structured environments (broth growth versus plaque growth); low versus high phage multiplicity Single-step growth; adsorption curves; kinetics of phage decay
Community ...a partner in coevolution Phage-host coevolution; inverse relationship between phage and uninfected-host density; community stability; host resistance; phage host-range breadth and variation; transduction and phage (lysogenic) conversion; competition among different phage species Phage-host continuous-culture or serial-transfer experiments; in situ observation and experiment
Ecosystem ...a lower trophic level Phage impact on ecosystem nutrient cycling and energy flow; short circuiting of microbial loop In situ observation and experiment

Phage Organismal Ecology

The basic phage life cycle. In the hierarchy of ecological disciplines, phage organismal ecology is most closely allied with the molecular (plus physiological and genetic) characterization of phages. While underlain by copious variety and details, the general phage life cycle (Figure 1) basically involves adsorption, infection, and release, plus considerations of phage decay. The study of these processes - especially from the perspective of in situ costs, benefits, expression, and per-infection productivity - is the province of the phage organismal ecologist. More broadly, one can view virus organismal ecology as the study of the adaptations viruses employ to overcome physical, chemical, or biological barriers to their transmission between hosts (44).

Figure 1: General Phage Life Cycle (below).

Phage adsorption. Phage adsorption begins after phage release from infected cells and ends with the uptake of phage genomes into the cytoplasm of adsorption-sensitive hosts. The more rapidly a phage adsorbs a permissive host cell, the greater its likelihood that it will avoid decay (e.g., 19,36,56) and the shorter its overall life cycle (5). Nevertheless, phage mutants displaying faster adsorption than wild type have been isolated from laboratory cultures (30). In addition, by requiring specific adsorption cofactors, some phages, such as phage T4, may be adsorption competent within environments in which healthy hosts are likely (e.g., colons) but adsorption incompetent (or less competent) in environments where healthy hosts are less likely (e.g., sewage) (28,47).

Infection (the latent period). The phage latent period begins with the eclipse, a period during which the artificial lysis of an infected host will not release infective phage particles. Post eclipse of a typical infection I refer to as a period of phage-progeny maturation. During this latter period either infected bacteria release mature phages without lysis (46) or artificial lysis results in the release of phage progeny (35). Maturation, for highly virulent phages, mostly occurs at a constant, linear rate rather than exponentially because the rate of synthesis of virion components is limited by some aspect of the host's anatomy or physiology (40,68). Things are complicated, however, if cells are able to continue to grow and divide during a phage infection since cell growth can increase in number whatever cell components are limiting. At the same time, the synthesis of phage components can have negative effects on host division. These negative effects range from a slowing of host population growth as seen with filamentous phages (46) to a complete cessation of host division as seen with highly virulent phages such as phage T4 (e.g., 2).

A further complication is the length of the period of progeny maturation. With lytic phages the timing of host lysis controls the length of this period, with the timing of lysis, in turn, under the control of phage genes and proteins (e.g., holins; 67). Host nutrition status (40,64,68), temperature (32), and physiological state vis-à-vis the standard bacterial growth curve or chemostat doubling times (7,55,61) can also impact on this timing as can phage-controlled processes such as lysis inhibition and lysis from without (1,2,3,4). In addition, among even synchronously infected cells, it has long been known that the overall duration of the phage latent period can vary within a single culture (13). Consequently, most phages during single-step growth display a non-instantaneous rise, which is the time over which a population of synchronously infected hosts display phage-induced lyses (32,61). Progeny maturation and rise periods associated with chronic (a.k.a., continuous or persistent) infections can be particularly long (46).

Phage-progeny release. So long as a virus particle remains inside an infected bacterium, then it is not free to acquire a new host. An infected host may display significant productivity in terms of the intracellular maturation of progeny virions, but such productivity can pale in comparison with the growth rates that phage populations may achieve via the exponential growth that phage-progeny release makes possible. For most phages the release of progeny phages coincides with the destruction of the parental infected cell (lysis; 67). For filamentous phages, that extrude their phage progeny across the host cell envelope, release does not necessarily result in host-cell death (46).

The phage progeny released from an individual bacterium are collectively referred to as a burst. For phage populations one typically determines a parameter know as burst size that is equal to the total number of phages produced by a single round of phage infection of host cells, divided by the total number of cells that had been infected prior to phage-progeny release. Measured burst size can vary considerably between individual infected cells (33) and even over the course of released-phage storage (20). Burst-size determination is complicated if hosts aggregate or fail to fully separate in culture (12) or if phage release occurs via a mechanism other than host lysis (7).

Phage decay. If one is willing to accept that phages are alive (e.g., 24), then phage decay is equivalent to virion death (a.k.a., "inactivation" or "loss of titer"; 36) or to a lack of infected-cell productivity without reduction to lysogeny. Phage decay (recently reviewed by 64,73) likely limits the impact of phages on bacteria (65) plus imposes important constraints on the evolution of non-temperate phages since it implies that virion populations cannot survive indefinitely in the absence of sufficient densities of susceptible bacteria (e.g., 27,71). Similarly, the evolution of lysogeny must be dependent at least in part on the relative importance of virion decay versus phage and prophage replication rates as, for example, Stewart and Levin (62) suggest with their "hard times" hypothesis.

Phage Population Ecology

Phage population growth. While phage organismal ecology emphasizes per-infection-productivity and phage community ecology has a host-population-dynamics emphasis, the emphasis of phage population ecology (Table 1) is on phage population growth either within bacteria cultures (5) or within individual infected bacteria (25). Like any organism living within a suitable environment possessing sufficient resources, a phage population will increase in number exponentially over time. Phage exponential growth is especially tractable during phage growth within liquid culture (2,21,32). Phage populations that increase in size most quickly should acquire host cells most rapidly. The acquisition (exploitation) of one bacterium by one phage means that one-less unit of bacteria resource is available for exploitation by a second phage. Over the short term, in relatively simple environments, selection within phage populations therefore should be for both more-rapid population growth and more-rapid host-cell acquisition.

Phage latent-period evolution. Certain phage characteristics should contribute to faster phage population growth (e.g., 31). For instance, we should expect evolution to favor decay-resistant virions, rapid adsorption (though, during plaque growth, not necessarily; see below), short eclipse periods (except given selection for pseudolysogeny or true lysogeny), high rates of progeny maturation (balanced, in some cases, e.g., with filamentous phages, against damage to the host resource), and, once initiated, rapid progeny release (ditto). With or without caveats, conspicuously absent from this list is the duration of phage latent periods and periods of progeny maturation, with the length of both a function of lysis timing. Here I consider forces that impact the evolutionary optimization of the duration of phage latent periods.

From an ecological perspective we can distinguish the members of populations into three groups: prereproductive, reproduction, and postreproductive. Postreproductive phages, variously defined, are irrelevant to this discussion. Prereproductive phages are those engaged in either adsorption (including the extracellular search for susceptible bacteria) or the eclipse, since during these periods the phage is not generating mature phage progeny. Reproductive phages are those infecting bacteria during the phage period of progeny maturation. For phages that must lyse their host bacteria to disseminate phage progeny, we may describe a period of progeny maturation as optimal in duration should the latent period giving rise to it result in maximized phage-population growth rates. Too-short latent periods result in insufficient burst sizes to sustain maximal phage population growth while too-long latent periods slow phage population growth by delaying phage-progeny acquisition of new host bacteria.

When prereproductive periods are short, this means that free phages can rapidly find uninfected cells and then rapidly gear up for intracellular progeny maturation. Such conditions should select for rapid infection turnover (short latent periods) such that phage progeny acquire uninfected hosts before those cells are obtained by competing phages. In general then, high host densities and short phage eclipse periods should select for shorter phage latent periods (5). When prereproductive periods are long, by contrast, the reproductive period, once begun, is more valuable thereby resulting in selection for increased per-infection productivity. Thus, low host densities or long phage eclipse periods should select for larger phage burst sizes even at the expense of longer phage latent periods (5).

Contribution of early adsorbers. The impact of changes in host density on phage population growth and latent-period evolution are not as straightforward as one might expect given that a phage cohort's mean time until bacteria adsorption varies directly with host density (Figure 2B). The reason for this complication is a consequence of phage adsorption occurring essentially as an exponential decay in free-phage density (Figure 2A). For any phage cohort released at a given moment into a population of hosts, phage adsorption occurs such that some constant fraction of remaining free phages will adsorb over any given interval. As a consequence, more phages from a given cohort will adsorb during a sooner interval compared with some later interval.

Figure 2A: Exponential phage adsorption and phage population growth (below). Free-phage adsorption (e.g., 5) with log(N = per ml host density) indicated for different curves and k (the phage adsorption constant) = 2.5 x 10-9 ml/min. Adsorption curves cross the horizontal line at the average phage adsorption time (mean free time) = 1/kN. [Goto 2A, 2B, 2C, 2D, or all four]

Figure 2B: Exponential phage adsorption and phage population growth (below). Mean free time graphed as a function of bacteria density. [Goto 2A, 2B, 2C, 2D, or all four]

If by chance a phage adsorbs to a host earlier rather than later, then the duration that this phage is prereproductive will be shorter and therefore the total duration of that phage's life cycle will also be shorter. The rate of phage population growth is a function of the duration of the phage life cycle, as well as the per-host burst size. Furthermore, earlier-adsorbing phages are potentially greater in number due to the exponential kinetics of phage adsorption plus spend less time susceptible to non-adsorption-related virion decay (above). Consequently, it stands to reason that earlier-adsorbing members of phage-adsorption cohorts will contribute more to the exponential growth of a phage population than later-adsorbing members.

At greater host densities all phages adsorb relatively rapidly such that the variance in phage pre-reproduction duration is not large. However, at lower host densities the timing of the adsorption of the majority of a phage cohort is spread over much longer intervals (Figure 2A), and the contribution of those phages that by chance adsorb hosts earlier becomes increasingly large and important to overall phage population growth. Thus, the average timing of phage adsorption (the phage mean free time; see 5) may very well decline as a direct function of host density (Figure 2B), but phage population growth as a function of host density does not decline as quickly (Figure 2C). This means that while evolution ought to favor phages with longer periods of progeny maturation as host densities decline, the phage latent period that is optimal for phage-population exponential growth should not increase as fast as host densities decline (5; Figure 2D).

Figure 2C: Exponential phage adsorption and phage population growth (below). Log phage density following 1000-min of phage growth as simulated or calculated at different host densities (log-scale and log-transformation are both intentional as presented). A latent period of 25 min, burst size of 75 phages/cell, and adsorption constant as above were used. Simulations assumed exponential phage adsorption (circles) which is equivalent to the adsorption curves in panel A. For calculations it was assumed that individual free phages adsorb after an extracellular search of 1/kN min (squares) as calculated as a function of host density in Figure 2B. [Goto 2A, 2B, 2C, 2D, or all four]

Figure 2D: Exponential phage adsorption and phage population growth (below). Phage latent period that gives rise to maximal phage population growth determined using simulations (adsorption via exponential free-phage decline; circles) and calculations (adsorption for all of free-phage cohort is mean free time in duration; squares) as described for panel C (graph used with permission from ASM). See (5) for discussion of methods. [Goto 2A, 2B, 2C, 2D, or all four]

We would expect similar compromises to hold for phages that release their progeny via extrusion. For such phages, however, the important balance should be between (i) the kinetics of phage maturation and release, (ii) the impact of greater rates of phage release on infected-host replication, and (iii) the overall latent-period duration. For experiments addressing these issues for filamentous phages see (46) and for lytic phages see Abedon (in preparation).

Phage plaque growth. Phage growth may be observed within a simple, spatially structured environment as plaques punctuating an otherwise opaque bacteria lawn embedded within a soft-agar overlay. Phage growth in plaques may be considered to occur in four stages (45): (i) initial adsorption of seeded phages, (ii) initial round of infection, (iii) an "enlargement phase" which involves multiple rounds of adsorption, infection, and release, and (iv) the end of the enlargement phase which typically is associated with physiological changes in the bacteria lawn. Differences between phage growth in plaques versus broth occur throughout the enlargement phase during which the physical structure of solid media (i) slows both phage and host diffusion, (ii) prevents gross environmental mixing, and (iii) probably gives rise to local phage multiplicities that are much higher than one observes over the majority of phage growth in broth. Phage growth within plaques additionally introduces plaque size as a means by which issues of phage fitness may be addressed (e.g., 49,50).

We can imagine at least five selective pressures that act on phages during plaque growth: (i) At the periphery of plaques there should be selection for more-rapid exponential growth, e.g., short phage latent periods when host densities are high (above); (ii) regardless of location within a plaque, during the plaque enlargement phase there should be selection for fast diffusion away from the plaque center such that uninfected hosts surrounding the plaque may be obtained and exploited (essentially the same argument as many suggested explained the classic observation that smaller phages should make larger plaques than larger phages; e.g., 72); (iii) towards the center of plaques - where there is a low prevalence of uninfected hosts - there should also exist a countering selection for greater burst sizes even at the expense of longer latent periods; (iv) throughout the plaque there should be selection exerted by the tendency of phages to decay (48) including by processes of adsorption to cell debris or adsorption to infected cells (the latter due to superinfection exclusion; 3); and (v) there can be selection for maintenance of phage growth despite the physiological aging of the bacterial lawn (e.g., phage T7; 50). Given this myriad complexity, how, where, and when one determines phage fitness during plaque growth is extremely important since different plaque regions may be under different selective pressures that can vary over the course of plaque development.

As a further complication, plaque size does not necessarily correlate with per-infection productivity. It has been hypothesized, for instance, that phages displaying shorter latent periods, even given smaller burst sizes, could display larger plaques (45,74). Longer latent periods resulting in smaller plaque sizes are most commonly (and classically) observed among T-even phages where lysis-inhibition defective (r) mutants display larger plaques and conditionally shorter latent periods than lysis-inhibition competent wild-type phages (34,43). I have also observed larger plaques with phage RB69 (also T-even-like; 8) that appear to be a consequence of reductions in phage latent periods (and burst size) rather than due to changes in phage adsorption rates or other increases in per-infection productivity (Abedon, in preparation). It has additionally been hypothesized (45,74) that reducing host-attachment efficiency given phage-host collision can increase rates of plaque enlargement since with slower adsorption phages might spend less time infecting cells and more time diffusing towards the periphery of plaques. Indeed, one explanation for why phage l lost its tail fiber upon domestication (42) is that reduced adsorption efficiency resulted in the formation of inescapably selectable larger plaques. Sarma and Kuar (60) observed perhaps similar results with cyanophage N-1.

Phage community ecology

Community stability. Phage community ecology (Table 1) emphasizes the bacteria host, e.g., the impact of phages on bacteria densities and the evolution of phage resistance (10,16). Phage community ecology also considers phage-host coevolution, such as the propensity for phages to evolve strategies that counter mechanisms of host resistance. Bacteria evolution of phage resistance can contribute to the stability of phage-containing communities by impeding bacteria extinction. Stability additionally refers to the range in densities of host and phage populations as they oscillate over time, with greater oscillation amplitude (density variance) corresponding to lower community stability.

Phage community stability in the laboratory typically is studied within continuous phage-bacteria cocultures that are commonly, though when phages are present not necessarily correctly (58) referred to as chemostats. A chemostat possesses a reservoir containing sterile media connected to a well-mixed growth vessel containing microorganisms. Flow from reservoir to growth vessel may be controlled via the use of a peristaltic pump, with outflow from the growth vessel occurring at the same rate as inflow. Phage-host communities within chemostats often are more stable than may be accounted for by phage community ecology theory (16,61). In Figure 3A I present a simulation of a relatively unstable chemostat. Note that phages have driven phage-sensitive bacteria to extinction (<10-2/ml) after about 110 hours of chemostat progression and that, due to outflow from the chemostat growth chamber, phages then decline to extinction about 100 hours later.

Figure 3A: Computer-simulated chemostats (below). Chemostats were simulated employing the method and parameter values of Bohannan and Lenski (14). Time steps here are 1 min rather than 3 min; the initial host and phage densities are 104/ml and 105/ml, respectively; and unless otherwise noted (in subsequent simulations) the limiting nutrient is glucose which is found in the chemostat reservoir at a density of 0.5 mg/liter. Bacteria are presented as solid lines and phages as dotted lines. Phage and bacteria densities during simulations were sampled for inclusion in graphs once every 30 min. These simulated chemostats contain no phage-resistant bacteria or other bacteria refuges from phage attack. Extinction is assumed to occur at or below densities of 10-2/ml. Bacteria are presented as solid lines and phages as dotted lines. [Goto 3A, 3B, 3C, 3D, or all four]

Refuges. Levin et al. (52) speculated that refuges for sensitive bacteria away from phage attack could increase the stability of phage-host communities, as subsequent experiments have corroborated (61). In such a scheme the extinction of sensitive bacteria is prevented by their hiding, for example, within chemostat wall populations. Following phage-induced lysis of host populations, presumably only those sensitive hosts survive that remain in hiding. Through cell division, these hosts can supply sensitive hosts to the liquid (unrefuged) phase of the chemostat. Once phage populations have declined, due to their outflow from the chemostat, the liquid-phase host populations can grow back to higher population densities.

Slowed adsorption. Bohannan and Lenski (15) describe bacteria that have entered a "genetic" refuge (phage-resistant mutants) as "invulnerable prey". However, since unless a phage's collision with a bacterium results in some degree of phage-host attachment, then a resistant bacterium is not potential prey but instead some relatively inert component of the environment off of which phages "bounce." Wilkinson (70), on the other hand, has suggested a model in which completely resistant bacteria really are invulnerable prey. Here the assumption is that the "predator" species (in this case a Bdellovibrio) may reversible interact with non-prey bacteria by pausing following collision. This delay in detachment extends the bdellovibrio's extracellular search. From the perspective of susceptible bacteria, this delay is equivalent to a reduction in the effective predator density. Wilkinson's conclusion upon modeling such a system is that the presence of non-prey bacteria, even in the absence of metabolic competition with prey bacteria, will result in a stabilization of sensitive-bacteria population densities.

Reductions in phage adsorption rates could similarly result in increased community stability. A partial reduction in host reception to phage adsorption (e.g., T2-partially resistant bacteria, a.k.a.,"less vulnerable" bacteria), for instance, should contribute to an increase in community stability by delaying overall of phage-population attachment to sensitive bacteria (17). Consistently, Figure 3B presents a simulated chemostat for which the phage rate of adsorption has been reduced by one half, and bacteria and phage extinctions are thereby avoided. Again with T2 phages, there apparently is a tendency for these phages to be temporarily adsorption-inhibited (up to weeks at room temperature) following release from host cells (59). This phenomenon could also serve to increase community stability by delaying phage adsorption. Indeed, any host refuge from phage adsorption should reduce phage population productivity by reducing the effective host density (a "numerical" host refuge; 26,61), even if direct physical interactions between refuged (but otherwise phage-sensitive) hosts and free phages are nonexistant. By extension, mechanisms of phage decay, including outflow from chemostat growth chambers, should have the effect of reducing phage number, thereby increasing community stability. Furthermore, phage evolution that counters mechanisms that interfere with phage adsorption or decay should result in a decrease in community stability

Figure 3B: Computer-simulated chemostats (below). Figure shows the same chemostat as Figure 3A though with the phage adsorption constant reduced by one half. [Goto 3A, 3B, 3C, 3D, or all four]

Reduced phage productivity. Host density impacts on community stability by affecting the peak phage densities that follow community-wide host lysis. With more phages than hosts within a batch-culture system, eventually all sensitive bacteria may become adsorbed and lysed (11,26). However, in continuous culture there will be decay in free-phage densities due to outflow from the growth vessel. Consequently, since the rate that host cells are found by free phages is a function of free-phage density (1), there is a race between phage sensitive bacteria survival and free-phage outflow. The lower the peak phage density, the less the bacteria population will be reduced in size due to phage adsorption, and the greater the likelihood that phage adsorption will not reduce the bacteria population to the point of extinction (compare, for example, the peak phage densities in Figure 3A versus Figures 3C and 3D). The smaller the bacteria population available for infection within a chemostat, in turn, the lower the peak phage density (compare Figures 3A and 3C). Bohannan and Lenski (14) demonstrate this point by reducing the bacteria growth potential, through restrictions in the density of a limiting nutrient (glucose) within the nutrient reservoir, and then observing an increase in phage-bacteria community stability. See Figure 3C for a simulated chemostat in which the nutrient density in the chemostat nutrient reservoir has been reduced by one half and note again that the extinction of bacteria and phages is avoided.

Figure 3C: Computer-simulated chemostats (below). Figure shows the same chemostat as Figure 3A but with one-half as much limiting glucose. [Goto 3A, 3B, 3C, 3D, or all four]

The productivity of phage infections, along with their density, together determines peak phage densities. It is well known that phage growth parameters, such as burst size, can vary as a function of host physiology (discussed above). If the stability of chemostats is an inverse function of peak phage density (i.e., more phages = less stability), then reduced infection productivity given reduced nutrient availability should contribute to an increase in community stability (as I will demonstrate elsewhere with chemostat simulations; Abedon, in preparation). Similarly, we might expect that the T-even-phage lysis-inhibition phenotype (1,3) would be destabilizing since it contributes, particularly at higher host densities, to a larger phage burst size. In Figure 3D the impact on community stability of reducing the phage burst size by one-half is explored, with bacteria and phage extinction yet again avoided.

Figure 3D: Computer-simulated chemostats (below). Figure shows the same chemostat as Figure 3A except with the phage burst size reduced by one half. [Goto 3A, 3B, 3C, 3D, or all four]

Synthesis. It is highly likely that phage-host community stability arises from two relatively simple forces: (i) If sensitive hosts cannot be driven to extinction by even excess phage densities, e.g., as is at least approximated with host refuges from phage attack, then sensitive hosts simply will not be driven to extinction by phages. (ii) If sensitive hosts can be driven to extinction given sufficient phage densities, then hosts will be driven to extinction only if sufficient phage densities are present within an ecosystem. There are two corollaries to the second point: (a) At peak phage density, the fewer phages found within an ecosystem, the smaller the negative impact those phages will have on phage-susceptible bacteria populations and the more stable the system (compare Figure 3A with Figures 3C and 3D). (b) Mechanisms that interfere with a phage's attainment of higher peak densities (or with phage impact on individual bacteria) - e.g., more phage decay, more-rapid outflow, partial inhibition of phage adsorption, reduced phage burst sizes - may lead to an increase in the stability of a phage-bacteria community (ditto, plus Figure 3B). Indeed, as noted by E.S. Anderson in 1957 (p. 205) (11), "It is evident that suboptimal conditions for growth of the host cells may restrict phage multiplication in any environment, even when contacts between the virus and its host occur... Anything which restricts the phage titre limits the selective action of phage."

Phage ecosystem ecology

Phage ecosystem ecology (Table 1) encompasses the biotic as well as the abiotic world, in particular the biogeochemical cycling of nutrients and the flow of energy between and through ecosystems, usually with an aquatic emphasis (for recent reviews see 38,53,57,63,64,69,73). Bacteria consume, produce, and store nutrients and energy plus contribute to the decomposition of other organisms. Phage infections contribute to a solubilization of bacteria cells, whether following host-cell lysis or via the conversion of host components into virion particles. Solubilized bacteria, in addition to no longer functioning as consumers, producers, or decomposers, are also less available as food to bacteria grazers (protists or animals) that obtain their nutrients and energy through the ingestion or engulfment of intact bacteria. Since bacteria are the chief consumers of the water-solubilized components of especially aquatic ecosystems, a major consequence of the phage-induced lysis of bacteria is not just a reduction in the productivity of bacteria populations but also a delay in the movement up food chains of bacteria-contained nutrients and energy. Suttle (64) additionally argues that aspects of virus-induced cell lysis in aquatic environments can have significant positive and negative impacts on the abundance of various greenhouse gasses found within Earth's atmosphere.

In their requirement for intact bacteria, phages in a sense are competitors of the bacteria grazers. Due to the host-range constraints observed among all parasites, individual phages also tend to be more specialized than most grazers in terms of what bacteria within a community they may affect (e.g., 37,66). In addition, phages can make direct, positive contributions to the fitness of bacteria hosts through phage conversion or via the transduction of genes from other bacteria. Phage DNA and protein coats, following abortive infection, could even serve as a bacteria nutrient (38).

Phage ecosystem ecology also represents an elaboration on the various issues of organismal, population, and community ecology already discussed. It follows, therefore, that many or all of the complications, caveats, and considerations discussed throughout this review also affect our understanding of the phage impact on ecosystem nutrient cycling and energy flow. In addition, much of the impact of phages on ecosystems has been discerned from the study of aquatic phage biology. However, aquatic systems - since for the most part they are liquid rather than solid, can be moderately well mixed, and also can be quite large - are among the very simplest phage-containing ecosystems. We might expect that other ecosystems, for example soils (22) or biofilms (41), would display greater complexity in terms of the phage impact on nutrient cycling and energy flow. Thus, both literally and figuratively, our understanding of the impact of phages on real ecosystems has barely scratched the surface of phage ecosystem ecology's ultimate goal: Quantifying the impact of phages on nutrient cycling and energy flow throughout the biosphere.

References

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  61. Schrag, S. and J.E. Mittler. 1996. Host-parasite persistence: the role of spatial refuges in stabilizing bacteria-phage interactions. American Naturalist 148:348-347.
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Figure 2: Exponential phage adsorption and phage population growth (below).

Figure 3: Computer-simulated chemostats (below).

Submissions Archive

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Letters & Questions

Letters should consist of comments, short statements, or personal editorials. Send all letters to abedon.1@osu.edu or to "Letters", Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. Please send all letters in English and all mailed or attached letters as Microsoft Word documents, if possible (I'll let you know if I have trouble converting any other document formats). In addition, to standard letters, BEG receives questions on a regular basis that may be addressed by BEG members. These questions are listed below. Anybody interested in answering these questions through BEG News, e-mail me at the following address: abedon.1@osu.edu. Alternatively, answer by clicking the authors name. Please note that these questions have not been edited for grammar, spelling, or clarity.
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Phage Images

Please send any phage images that you would like to present in this section to "Phage Images," The Bacteriophage Ecology Group, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906. Alternatively, you may scan the images yourself and send them as an attachment to abedon.1@osu.edu. Please save all scans in gif or jpg formats and preferably with an image size (in terms of width, height, and kbytes) that will readily fit on a standard web page. No copyrighted material without permission, please!

T4 phage v1 by ~posidian

"T4 phage v1 by ~posidian", a.k.a., Joshua Orvis, Associate Director of Bioinformatics, University of Oklahoma Health Sciences Center, joshua-orvis@ouhsc.edu.

Phage Image Archive

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New Publications

New bacteriophage publications are listed below. Each quarter not-yet-listed publications from the previous two years will be presented along with their abstracts. The indicator "???" denotes, of course, that specific information is not yet in the BEG Bibliography. Please help in the compilation of the BEG Bibliography by supplying any updated information, correcting any mistakes, and, of course, sending the references to your bacteriophage ecology publications, as well as the references to any bacteriophage ecology publications that you know of but which are not yet in the bibliography (send to abedon.1@osu.edu or to "BEG Bibliography," Bacteriophage Ecology Group News, care of Stephen T. Abedon, Department of Microbiology, The Ohio State University, 1680 University Dr., Mansfield, Ohio 44906). Also, be sure to indicate any listed publications that you feel should not be presented in the BEG Bibliography. This list is also present with available abstracts at the end of BEG News.
  1. Distribution of virus-like particles in an oligotrophic marine environment (Alboran Sea, Western Mediterranean). Alonso, M. C., Jimenez-Gomez, F., Rodriguez, J., Borrego, J. J. (2001). Microbial Ecology 42:407-415. [PRESS FOR ABSTRACT]

  2. The bacteriophages of ruminal prevotellas. Ambrozic, J., Ferme, D., Grabnar, M., Ravnikar, M., Avgustin, G. (2001). Folia Microbiologica 46:37-39. [PRESS FOR ABSTRACT]

  3. Isolation and characterization of bacteriophage-resistant mutants of Vibrio cholerae O139. Attridge, S. R., Fazeli, A., Manning, P. A., Stroeher, U. H. (2001). Microbial Pathogenesis 30:237-246. [PRESS FOR ABSTRACT]

  4. Bacteriophage-bacteriophage interactions in the evolution of pathogenic bacteria. Boyd, E. F., Davis, B. M., Hochhut, B. (2001). Trends in Microbiology 9:137-144. [PRESS FOR ABSTRACT]

  5. Chemical and microbial characterization of household graywater. Casanova, L. M., Gerba, C. P., Karpiscak, M. (2001). J Environ Sci Health Part A Tox Hazard Subst Environ Eng 36:395-401. [PRESS FOR ABSTRACT]

  6. Microbial population dynamics and diversity during a bloom of the marine coccolithophorid Emiliania huxleyi (Haptophyta). Castberg, T., Larsen, A., Sandaa, R. A., Brussaard, C. P. D., Egge, J. K., Heldal, M., Thyrhaug, R., van Hannen, E. J., Bratbak, G. (2001). Marine Ecology Progress Series 221:39-46. [PRESS FOR ABSTRACT]

  7. Nucleotide sequence of coliphage HK620 and the evolution of lambdoid phages. Clark, A. J., Inwood, W., Cloutier, T., Dhillon, T. S. (2001). Journal of Molecular Biology 311:657-679. [PRESS FOR ABSTRACT]

  8. Bacteriophage T4 multiplication in an Escherichia coli biofilm. Corbin, B. D., Aron, G. M., McLeon, R. J. C. (2001). Canadian Journal of Microbiology 47:680-684. [PRESS FOR ABSTRACT]

  9. Progeny of the phage school. Dixon, B. (2001). ASM News 69:432-433. [PRESS FOR ABSTRACT]

  10. Direct and quantitative detection of bacteriophage by "hearing" surface detachment using a quartz crystal microbalance. Dultsev, F. N., Speight, R. E., Fiorini, M. T., Blackburn, J. M., Abell, C., Ostanin, V. P., Klenerman, D. (2001). Analytical Chemistry 73:3935-3939. [PRESS FOR ABSTRACT]

  11. Diminished diarrheal response to Vibrio cholerae strains carrying the replicative form of the CTXf genome instead of CTXf lysogens in adult rabbits. Faruque, S. M., Rahman, M. M., Hasan, A. K., Nair, G. B., Mekalanos, J. J., Sack, D. A. (2001). Infection and Immunity 69:6084-6090. [PRESS FOR ABSTRACT]

  12. Phage antibacterials make a comeback. Fischetti, V. A. (2001). Nature Biotechnology 19:734-735. [NO ABSTRACT]

  13. A conserved genetic module that encodes the major virion components in both the coliphage T4 and the marine cyanophage S-PM2. Hambly, E., Tétart, F., Desplats, C., Wilson, H., Krisch, H. M., Mann, N. H. (2001). Proceedings of the National Academy of Sciences, USA 98:11411-11416. [PRESS FOR ABSTRACT]

  14. Isolation and characterization of a temperature-sensitive generalized transducing bacteriophage for Vibrio cholerae. Hava, D. L., Camilli, A. (2001). J Microbiol Methods 46:217-225. [PRESS FOR ABSTRACT]

  15. Effects of concentrated viral communities on photosynthesis and community composition of co-occurring benthic microalgae and phytoplankton. Hewson, I., O'Neil, J. M., Heil, C. A., Bratbak, G., Dennison, W. C. (2001). Aquatic Microbial Ecology 25:1-10. [PRESS FOR ABSTRACT]

  16. Mosaic structure of shiga-toxin-2-encoding phages isolated from Escherichia coli O157:H7 indicates frequent gene exchange between lambdoid phage genomes. Johansen, B. K., Wasteson, Y., Granum, P. E., Brynestad, S. (2001). Microbiology 147:1929-1936. [NO ABSTRACT]

  17. Elimination of fecal coliforms and F-specific RNA coliphage from oysters (Crassostrea virginica) relaid in floating containers. Kator, H., Rhodes, M. (2001). Journal of Food Protection 64:796-801. [PRESS FOR ABSTRACT]

  18. Octamer-based genome scanning distinguishes a unique subpopulation of Escherichia coli O157:H7 strains in cattle. Kim, J., Nietfeldy, J., Benson, A. K. (2001). Proceedings of the National Academy of Sciences, USA 96:13288-13293. [PRESS FOR ABSTRACT]

  19. Antacid increases survival of Vibrio vulnificus and Vibrio vulnificus phage in a gastrointestinal model. Koo, J., Marshall, D. L., Depaola, A. (2001). Applied and Environmental Microbiology 67:2895-2902. [PRESS FOR ABSTRACT]

  20. [Vibrio cholerae O139 bacteriophages]. Kudriakova, T. A., Makedonova, L. D., Kachkina, G. V., Saiamov, S. R. (2001). Zhurnal Mikrobiologii, Epidemiologii i Immunobiologii 28-30. [PRESS FOR ABSTRACT]

  21. Population dynamics and diversity of phytoplankton, bacteria and viruses in a seawater enclosure. Larsen, A., Castberg, T., Sandaa, R. A., Brussaard, C. P. D., Egge, J. K., Heldal, M., Paulino, A., Thyrhaug, R., van Hannen, E. J., Bratbak, G. (2001). Marine Ecology Progress Series 221:47-57. [PRESS FOR ABSTRACT]

  22. Viruses in the plankton of freshwater and saline Antarctic lakes. Laybourn-Parry, J., Hofer, J. S., Sommaruga, R. (2001). Freshwater Biology 46:1279-1287. [PRESS FOR ABSTRACT]

  23. Examination of bacteriophage as a biocontrol method for salmonella on fresh-cut fruit: a model study. Leverentz, B., Conway, W. S., Alavidze, Z., Janisiewicz, W. J., Fuchs, Y., Camp, M. J., Chighladze, E., Sulakvelidze, A. (2001). Journal of Food Protection 64:1116-1121. [PRESS FOR ABSTRACT]

  24. Colloidal interactions in suspensions of rods. Lin, K., Crocker, J. C., Zeri, A. C., Yodh, A. G. (2001). Phys Rev Lett 87:088301. [PRESS FOR ABSTRACT]

  25. Depolymerization of the capsular polysaccharide from Vibrio cholerae O139 by a lyase associated with the bacteriophage JA1. Linnerborg, M., Weintraub, A., Albert, M. J., Widmalm, G. (2001). Carbohydrate Research 333:263-269. [PRESS FOR ABSTRACT]

  26. Physiological function of exopolysaccharides produced by Lactococcus lactis. Looijesteijn, P. J., Trapet, L., de, Vries E., Abee, T., Hugenholtz, J. (2001). International Journal of Food Microbiology 64:71-80. [PRESS FOR ABSTRACT]

  27. Distribution, isolation, host specificity, and diversity of cyanophages infecting marine Synechococcus spp. in river estuaries. Lu, J., Chen, F., Hodson, R. E. (2001). Applied and Environmental Microbiology 67:3285-3290. [PRESS FOR ABSTRACT]

  28. Elution, detection, and quantification of polio I, bacteriophages, Salmonella montevideo, and Escherichia coli O157:H7 from seeded strawberries and tomatoes. Lukasik, J., Bradley, M. L., Scott, T. M., Hsu, W. Y., Farrah, S. R., Tamplin, M. L. (2001). Journal of Food Protection 64:292-297. [PRESS FOR ABSTRACT]

  29. The genome of archaeal prophage PsiM100 encodes the lytic enzyme responsible for autolysis of Methanothermobacter wolfeii. Luo, Y., Pfister, P., Leisinger, T., Wasserfallen, A. (2001). Journal of Bacteriology 183:5788-5792. [PRESS FOR ABSTRACT]

  30. Sequence analysis and molecular characterization of the Lactococcus lactis temperate bacteriophage BK5-T. Mahanivong, C., Boyce, J. D., Davidson, B. E., Hillier, A. J. (2001). Applied and Environmental Microbiology 67:3564-3576. [PRESS FOR ABSTRACT]

  31. Growth and survival of clinical vs. environmental species of Aeromonas in tap water. Mary, P., Buchet, G., Defives, C., Hornez, J. P. (2001). International Journal of Food Microbiology 69:191-198. [PRESS FOR ABSTRACT]

  32. Livestock deaths associated with Clavibacter toxicus/Anguina sp. infection in seedheads of Agrostis avenacea and Polypogon monspeliensis. McKay, A. C., Ophel, K. M., Reardon, T. B., Gooden, J. M. (2001). Plant Disease 77:635-641. [PRESS FOR ABSTRACT]

  33. Characterization of two novel Rhizobium leguminosarum bacteriophages from a field release site of genetically-modified rhizobia. Mendum, T. A., Clark, I. M., Hirsch, P. R. (2001). Antonie van Leeuwenhoek 79:189-197.

  34. Effect of phage on survival of Salmonella enteritidis during manufacture and storage of cheddar cheese made from raw and pasteurized milk. Modi, R., Hirvi, Y., Hill, A., Griffiths, M. W. (2001). Journal of Food Protection 64:927-933. [PRESS FOR ABSTRACT]

  35. Phage conversion of Panton-Valentine leukocidin in Staphylococcus aureus: molecular analysis of a PVL-converting phage, phiSLT. Narita, S., Kaneko, J., Chiba, J., Piemont, Y., Jarraud, S., Etienne, J., Kamio, Y. (2001). Gene 268:195-206. [PRESS FOR ABSTRACT]

  36. Increased mutation rate of E. coli K12 lambda cultures maintained in continuous logarithmic growth. Northrop, J. H. (2001). Journal of General Physiology 50:369-377. [PRESS FOR ABSTRACT]

  37. Pathogenicity and resistance islands of staphylococci. Novick, R. P., Schlievert, P., Ruzin, A. (2001). Microbes Infect 3:585-594. [PRESS FOR ABSTRACT]

  38. Diversification of Escherichia coli genomes: are bacteriophages the major contributors? Ohnishi, M., Kurokawa, K., Hayashi, T. (2001). Trends in Microbiology 9:481-485. [PRESS FOR ABSTRACT]

  39. Bacteriophage P4282, a parasite of Ralstonia solanacearum, encodes a bacteriolytic protein important for lytic infection of its host. Ozawa, H., TANAKA, H., Ichinose, Y., Shiraishi, T., Yamada, T. (2001). MGG Molecular Genetics and Genomics 265:95-101.

  40. Survival of bacteriophages of Lactococcus lactis in sodium hypochlorite and during storage. Parada, J. L., De Fabrizio, S. V. (2001). Revista Argentina de Microbiologia 33:89-95.

  41. Comparative study of nine Lactobacillus fermentum bacteriophages. Picozzi, C., Galli, A. (2001). Journal of Applied Microbiology 91:394-403.

  42. Evolutionary role of restriction/modification systems as revealed by comparative genome analysis. Rocha, E. P., Danchin, A., Viari, A. (2001). Genome Research 11:946-958. [PRESS FOR ABSTRACT]

  43. Changes in bacterial community composition and dynamics and viral mortality rates associated with enhanced flagellate grazing in a mesoeutrophic reservoir. Simek, K., Weinbauer, M. G., Hornak, K., Dolan, J. R., Nedoma, J., Masin, M., Amann, R. (2001). Applied and Environmental Microbiology 67:2723-2733. [NO ABSTRACT]

  44. Quorum sensing is a global regulatory mechanism in enterohemorrhagic Escherichia coli O157:H7. Sperandio, V, Torres, A. G., Giron, J. A., Kaper, J. B. (2001). Journal of Bacteriology 183:5187-5197. [PRESS FOR ABSTRACT]

  45. Application of Streptococcus thermophilus DPC1842 as an adjunct to counteract bacteriophage disruption in a predominantly lactococcal Cheddar cheese starter: use in bulk starter culture systems. Stokes, D., Ross, R. P., Fitzgerald, G. F., Coffey, A. (2001). Lait 81:327-334. [PRESS FOR ABSTRACT]

  46. Therapy of infections in cancer patients with bacteriophages. Weber-Dabrowska, B., Mulczyk, M., Górski, A. (2001). CLIN APPL IMMUNOL REV 1:131-134. [PRESS FOR ABSTRACT]

  47. Interaction of the PhiHSIC virus with its host: lysogeny or pseudolysogeny? Williamson, S. J., McLaughlin, M. R., Paul, J. H. (2001). Applied and Environmental Microbiology 67:1682-1688. [PRESS FOR ABSTRACT]

  48. Integrated management of bacterial leaf spot of mungbean with bacteriophages of Xav and chemicals. Borah, P. K., Jindal, J. K., Verma, J. P. (2000). Journal of Mycology and Plant Pathology 30:19-21.

  49. Viruses of fungi and protozoans: Is everyone sick? Bruenn, J. A. (2000). pp. 297-317 in Hurst, C. J. (ed.) Viral Ecology. Academic Press, San Diego. [NO ABSTRACT]

  50. Lateral gene transfer in prokaryotes. Campbell, A. M. (2000). Theoretical Population Biology 57:71-77. [PRESS FOR ABSTRACT]

  51. An introduction to the evolutionary ecology of viruses. DeFilippis, V. R., Villarreal, L. P. (2000). pp. 125-208 in Hurst, C. J. (ed.) Viral Ecology. Academic Press, San Diego. [NO ABSTRACT]

  52. Microvirus of Chlamydia psittaci strain Guinea pig inclusion conjunctivitis: Isolation and molecular characterization. Hsia, R. C., Ting, L. M., Bavoil, P. M. (2000). Microbiology (Reading) 146:1651-1660.

  53. Genomic sequences of bacteriophages HK97 and HK022: Pervasive genetic mosaicism in the lambdoid bacteriophages. Juhala, R. J., Ford, M. E., Duda, R. L., Youlton, A., Hatfull, G. F., Hendrix, R. W. (2000). Journal of Molecular Biology 299:27-51.

  54. Ecology of bacteriophages in nature. Paul, J. H., Kellogg, C. A. (2000). pp. 211-246 in Hurst, C. J. (ed.) Viral Ecology. Academic Press, San Diego. [NO ABSTRACT]

  55. Genomic sequence and analysis of the atypical temperate bacteriophage N15. Ravin, V, Ravin, N., Casjens, S., Ford, M. E., Hatfull, G. F., Hendrix, R. W. (2000). Journal of Molecular Biology 299:53-73.

  56. Comparative analysis of Chlamydia bacteriophages reveals variation localized to a putative receptor binding domain. Read, T. D., Fraser, C. M., Hsia, R. C., Bavoil, P. M. (2000). Microbial and Comparative Genomics 5:223-231.

  57. The passage and propagation of fecal indicator phages in birds. Ricca, D. M., Cooney, J. J. (2000). Journal of Industrial Microbiology & Biotechnology. 24:127-131.

  58. Screening environmental samples for source-specific bacteriophage hosts using a method for the simultaneous pouring of 12 petri plates. Ricca, D. M., Cooney, J. J. (2000). Journal of Industrial Microbiology & Biotechnology. 24:124-126.

  59. The genome sequence of the plant pathogen Xylella fastidiosa. Simpson, A. J. G., Reinach, F. C., Arruda, P., Abreu, F. A., Acencio, M., Alvarenga, R., Alves, L. M. C., Araya, J. E., Baia, G. S., Baptista, C. S., Barros, M. H., Bonaccorsi, E. D., Bordin, S., Bove, J. M., Briones, M. R. S., Bueno, M. R. P., Camargo, A. A., Camargo, L. E. A., Carraro, D. M., Carrer, H., Colauto, N. B., Colombo, C., Costa, F. F., Costa, M. C. R., Costa-Neto, C. M., Coutinho, L. L., Cristofani, M., Dias-Neto, E., Docena, C., El-Dorry, H., Facincani, A. P., Ferreira, A. J. S., Ferreira, V. C. A., Ferro, J. A., Fraga, J. S., Franca, S. C., Franco, M. C., Frohme, M., Furlan, L. R., Garnier, M., Goldman, G. H., Goldman, M. H. S., Gomes, S. L., Gruber, A., Ho, P. L., Hoheisel, J. D., Junqueira, M. L., Kemper, E. L., Kitajima, J. P., Krieger, J. E., Kuramae, E. E., Laigret, F., Lambais, M. R., Leite, L. C. C., Lemos, E. G. M., Lemos, M. V. F., Lopes, S. A., Lopes, C. R., Machado, J. A., Machado, M. A., Madeira, A. M. B. N., Madeira, H. M. F., Marino, C. L., Marques, M. V., Martins, E. A. L., Martins, E. M. F., Matsukuma, A. Y., Menck, C. F. M., Miracca, E. C., Miyaki, C. Y., Monteiro-Vitorello, C. B., Moon, D. H., Nagai, M. A., Nascimento, A. L. T. O., Netto, L. E. S., Nhani, A., Jr., Nobrega, F. G., Nunes, L. R., Oliveira, M. A., de Oliveira, M. C., de Oliveira, R. C., Palmieri, D. A., Paris, A., Peixoto, B. R., Pereira, G. A. G., Pereira, H. A., Jr., Pesquero, J. B., Quaggio, R. B., Roberto, P. G., Rodrigues, V, de, M. R., de Rosa, V. E., Jr., de Sa, R. G., Santelli, R. V., Sawasaki, H. E., da Silva, A. C. R., da Silva, A. M., da Silva, F. R., Silva, W. A., Jr., da Silveira, J. F. (2000). Nature (London) 406:151-157.

  60. Prophage, phiPV83-pro, carrying panton-valentine leukocidin genes, on the Staphylococcus aureus P83 chromosome: comparative analysis of the genome structures of phiPV83-pro, phiPVL, phi11, and other phages. Zou, D., Kaneko, J., Narita, S., Kamio, Y. (2000). Bioscience, Biotechnology, and Biochemistry 64:2631-2643. [PRESS FOR ABSTRACT]

  61. Flow cytometric analyses of virus infection in two marine phytoplankton species, Micromonas pusilla (Prasinophyceae) and Phaeocystis pouchetii (Prymnesiophyceae). Brussaard, C. P. D., Thyrhaug, R., Marie, D., Bratbak, G. (1999). Journal of Phycology 35:941-948. [PRESS FOR ABSTRACT]

  62. Biocontrol of Erwinia amylovora using bacteriophage. Gill, J. J., Svircev, A. M., Myers, A. L., Castle, A. J. (1999). Phytopathology 89:S27. [NO ABSTRACT]

  63. Cyanophages. Martin, E. L., Kokjohn, T. A. (1999). pp. 324-332 in Granoff, A., Webster, R. G. (eds.) Encyclopedia of Virology second edition. Academic Press, San Diego. [NO ABSTRACT]

  64. Bacteriophage therapy of Clostridium difficile-associated intestinal disease in a hamster model. Rdamesh, V., Fralick, J. A., Rolfe, R. D. (1999). Miroecol. Anarobes[sic?] 5:69-??? [NO ABSTRACT]

  65. Dissolved esterase activity as a tracer of physoplankton lysis: Evidence of high phytoplankton lysis rates in the northwestern Mediteranean. Agustí, S., Satta, M. P., Mura, M. P., Benavent, E. (1998). Limnology and Oceanography 43:1836-1849. [PRESS FOR ABSTRACT]

  66. Polyvirulent rhizobiophage from a soybean rhizosphere soil. Ali, F. S., Hammand, A. M. M., Loynachan, T. E. (1998). Soil Biology and Biochemistry 30:2171-2175. [NO ABSTRACT]

  67. Viral lysis of Phaeocystis pouchetii and bacterial secondary production. Bratbak, G., Jacobsen, A., Heldal, M. (1998). Aquatic Microbial Ecology 16:11-16. [PRESS FOR ABSTRACT]

  68. Virus production in Phaeocystis pouchetii and its relation to host cell growth and nutrition. Bratbak, G., Jacobsen, A., Heldal, M., Nagasaki, K., Thingstad, T. F. (1998). Aquatic Microbial Ecology 16:1-9. [NO ABSTRACT]

  69. Ultrastructural analysis of viral invection in the brown-tide alga, Aureococcus anophagefferens (Pelagophyceae). Gastrich, M. D., Anderson, O. R., Benmayor, S. S., Cosper, E. M. (1998). Phycologia 37:300-306. [PRESS FOR ABSTRACT]

  70. Biological control of bacterial blight of geranium with h-mutant bacteriophages. Harbaugh, B. K., Jones, J. B., Jackson, L. E., Somodi, G., Flaherty, J. E. (1998). 95th Annual International Conference of the American Society for Horticultural Science 33:519. [NO ABSTRACT]

  71. Effect of temperature on the algicidal activity and the satability of HaV (Heterosigma akashiwo virus). Nagasaki, K., Yamaguchi, M. (1998). Aquatic Microbial Ecology 15:211-216. [PRESS FOR ABSTRACT]

  72. Lysogeny of Oenococcus oeni (syn. Leuconostoc oenos) and study of their induced bacteriophages. Poblet-Icart, M., Bordons, A., Lonvaud-Funel, A. (1998). Current Microbiology 36:365-369.

  73. Comparative analysis of the effect of energy process inhibitors on the efficacy of phage infection in staphylococci. Polishko, T. N. (1998). Mikrobiolohichnyi Zhurnal 60:36-42.

  74. Seasonal abundance in Skagerrak-Kattegat coastal waters and host specificity of viruses infecting the marine photosynthetic flagellate Micromonas pusilla. Sahlsten, E. (1998). Aquatic Microbial Ecology 16:103-108. [PRESS FOR ABSTRACT]

  75. Vertical distribution of virus-like particles (VLP) and viruses infecting Micromonas pusilla during late summer in the southeastern Skagerrak. Sahlsten, E., Karlson, B. (1998). J. Plankton Res. 20:2207-2212. [PRESS FOR ABSTRACT]

  76. Morphology and abundance of free and temperate viruses in Lake Superior. Tapper, M. A., Hicks, R. E. (1998). Limnology and Oceanography 43:95-103. [PRESS FOR ABSTRACT]

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New Publications with Abstracts

For your convenience, a list of new publications without associated abstracts (but with links to abstracts) is found above. The list presented below is identical to the above list except that abstracts are included.
  1. Distribution of virus-like particles in an oligotrophic marine environment (Alboran Sea, Western Mediterranean). Alonso, M. C., Jimenez-Gomez, F., Rodriguez, J., Borrego, J. J. (2001). Microbial Ecology 42:407-415. Viruses are abundant in a variety of aquatic environments, often exceeding bacterial abundance by one order of magnitude. In the present study, the spatial distribution of viruses in offshore waters of the Alboran Sea (Western Mediterranean) have been studied to determine the relationships between viruses and host communities in this oligotrophic marine environment. Viral abundance was determined using two methods: (i) epifluorescence light microscopy using the dsDNA binding fluorochrome DAPI, and (ii) direct counts by transmission electron microscopy (TEM). The results obtained were significantly different; the highest viral counts were obtained by mean of TEM analyses. In all the samples tested the number of viruses was exceeded by the bacterial concentrations, with a ratio between viral and bacterial titers varying between 1.4 and 20. VLP (virus-like particle) counts were not significantly correlated (p>0.001) with chlorophyll a concentration or the abundance of cyanobacteria. However, there was a positive and significant correlation with bacterial abundance (p<0.001). The analysis of size and morphology of viral particles by TEM and the correlation obtained between the numbers of VLP and bacteria suggest that the majority of the viral particles in the Alboran Sea are bacteriophages. None of the indirect evidence suggested that eukaryotic algae or cyanobacteria were important host organisms in these waters.

  2. The bacteriophages of ruminal prevotellas. Ambrozic, J., Ferme, D., Grabnar, M., Ravnikar, M., Avgustin, G. (2001). Folia Microbiologica 46:37-39. Rumen bacteriophage-lyzed bacterial strains of the genus Prevotella were isolated and preliminarily characterized. The strain TCl-1 the species P. bryantii was the only prevotella strain successfully infected with filter sterilized rumen fluid from a black-and-white Holstein cow. Two types of plaques were observed, both rather small and turbid. Preliminary electron microscopy observation showed that several morphologically different bacteriophages were present in these plaques. The plaque eluates were further used for the infection of other prevotella strains. The plaques produced by the bacteriophages were observed with two strains, i.e. P. bryantii B(1)4 and P. brevis GA33. The bacteriophages from both strains were examined by transmission electron microscopy and several morphologically different bacteriophages were observed, among others also a large virion with an icosahedral head with the diameter of approximately 120 nm. The bacteriophage was identified in plaques of bacterial cells of the strain GA33 and has an approximately 800 nm long helical tail, which places it among the largest ruminal bacteriophages described to date. Other bacteriophages from the same indicator strain as well as from P. bryantii B(1)4 strain were smaller and tail structures were not observed in all of them

  3. Isolation and characterization of bacteriophage-resistant mutants of Vibrio cholerae O139. Attridge, S. R., Fazeli, A., Manning, P. A., Stroeher, U. H. (2001). Microbial Pathogenesis 30:237-246. Vibrio cholerae O139 strains produce a capsule which is associated with complement resistance and is used as a receptor by bacteriophage JA1. Spontaneous JA1-resistant mutants were found to have several phenotypes, with loss of capsule and/or O-antigen from the cell surface. Determination of the residual complement resistance and infant mouse colonization potential of each mutant suggested that production of O-antigen is of much greater significance than the presence of capsular material for both of these properties. Two different in vitro assays of complement resistance were compared and the results of one shown to closely reflect the comparative recoveries of bacteria from the colonization experiments. Preliminary complementation studies implicated two rfb region genes, wzz and wbfP, as being essential for the biosynthesis of capsule but not O-antigen

  4. Bacteriophage-bacteriophage interactions in the evolution of pathogenic bacteria. Boyd, E. F., Davis, B. M., Hochhut, B. (2001). Trends in Microbiology 9:137-144. Many bacteriophages carry virulence genes encoding proteins that play a major role in bacterial pathogenesis. Recently, investigators have identified bacteriophage-bacteriophage interactions in the bacterial host cell that also contribute significantly to the virulence of bacterial pathogens. The relationships between the bacteriophages pertain to one bacteriophage providing a helper function for another, unrelated bacteriophage in the host cell. Accordingly, these interactions can involve the mobilization of bacteriophage DNA by another bacteriophage, for example in Escherichia coli, Vibrio coli and Staphylococcus aureus; the host receptor for one bacteriophage being encoded by another, as found in V. cholerae; and the presence of one bacteriophage potentiating the virulence properties of another bacteriophage, as found in V. cholerae and Salmonella enterica

  5. Chemical and microbial characterization of household graywater. Casanova, L. M., Gerba, C. P., Karpiscak, M. (2001). J Environ Sci Health Part A Tox Hazard Subst Environ Eng 36:395-401. In arid areas, the search for efficient methods to conserve water is of paramount importance. One of the methods of water conservation available today is graywater recycling--the reuse of water from the sinks, showers, washing machine, and dishwasher in a home. The purpose of this project was to characterize the chemical and microbial quality of graywater from a single-family home with two adults. Water samples from a graywater holding tank were analyzed over a seven-month period for total coliforms, fecal coliforms, fecal streptococci, Staphylococcus aureus (S. aureus), Pseudomonas aeruginosa (P. aeruginosa), and coliphages. The pH, turbidity, biological oxygen demand (BOD), suspended solids (SS), electrical conductivity (EC), sulfates (SO4), and chlorides (Cl) were also measured. The mean numbers of total coliforms, fecal coliforms, fecal streptococci, and P. aeruginosa were 8.03 x 107, 5.63 x 105, 2.38 x 102, and 1.99 x 104 CFU/100 mL, respectively. S. aureus and coliphages were not detected. In the chemical analysis, mean values of 7.47 for pH, 43 nephelometric turbidity units (NTU) for turbidity, 64.85 mg/L for BOD, 35.09 mg/L for SS, 0.43 mS/cm for EC, 59.59 mg/L for SO4, and 20.54 mg/L for Cl were measured. These data were compared to data taken in 1986 and 1987, when two adults and one child lived in the household. Analysis showed no statistically significant difference in levels of total coliforms and suspended solids between the two data sets. There were statistically significant differences in levels of fecal coliforms, pH, turbidity, chlorides, sulfates, and BOD between the two households. Fecal coliforms, turbidity, and BOD were higher in the household with two adults and one child. Levels of Cl, SO4, and pH were higher in the household with two adults

  6. Microbial population dynamics and diversity during a bloom of the marine coccolithophorid Emiliania huxleyi (Haptophyta). Castberg, T., Larsen, A., Sandaa, R. A., Brussaard, C. P. D., Egge, J. K., Heldal, M., Thyrhaug, R., van Hannen, E. J., Bratbak, G. (2001). Marine Ecology Progress Series 221:39-46. Several previous studies have shown that Emiliania huxleyi blooms and terminations have been succeeded by an increase in large virus-like particles (LVLP), strongly suggesting the bloom collapse was caused by viral lysis. However, due to methodological limitations, knowledge of how such blooms affect the rest of the microbial community is limited. In the current study we induced a bloom of E. huxleyi in seawater enclosures and applied methods enabling us to describe the algae, bacteria and virus communities with greater resolution than has been done previously, The development of the dominating algal, viral and bacterial populations in the nutrient-amended seawater enclosures was followed by flow cytometry (FCM). Light microscopy (LM), PCR-denaturing gradient gel electrophoresis (PCR-DGGE) and pulsed-field gel electrophoresis (PFGE) were used to describe the changes in community composition in greater detail. The algal community was dominated by E. huxleyi until termination of the bloom by viral lysis, After bloom termination the additional algal populations present in the enclosures increased in abundance. A marked increase in viruses other than the one infecting E. huxleyi was also observed. Total bacterial number and community composition were also greatly influenced by the bloom and its collapse.

  7. Nucleotide sequence of coliphage HK620 and the evolution of lambdoid phages. Clark, A. J., Inwood, W., Cloutier, T., Dhillon, T. S. (2001). Journal of Molecular Biology 311:657-679. HK620 is a temperate lambdoid bacteriophage that adsorbs to the O-antigen of its host, Escherichia coli H. The genome of a temperature-sensitive clear-plaque mutant consists of 38,297 nucleotides in which we recognize 60 open reading frames (orfs). Eighteen of these lie in a region of the genome that we call the virion structure domain. The other 42 orfs lie in what we call the metabolic domain.Virions of HK620 resemble those of phage P22. The virion structural orfs encode three kinds of putative proteins relative to the virion proteins of P22: (1) those that are nearly (about 90 %) identical; (2) those that are weakly (about 30 %) identical; and (3) those composed of nearly and weakly identical segments. We hypothesize that these composite proteins form bridges between the virion proteins of the other two kinds.Three of the putative virion proteins that are only weakly identical to P22 proteins are 71, 60 and 79 % identical to proteins encoded by the phage APSE-1, whose virions also resemble those of P22. Because the hosts of APSE-1 and HK620 have been separated from each other by an estimated 200 My, we propose using the amino acid differences that have accumulated in these proteins to estimate a biological clock for temperate lambdoid phages.The putative transcriptional regulatory gene circuitry of HK620 seems to resemble that of phage lambda. Integration, on the other hand, resembles that of satellite phage P4 in that the attP sequence lies between the leftward promoter and int rather than downstream of int.Comparing the metabolic domains of several lambdoid phage genomes reveals seven short conserved sequences roughly defining boundaries of functional modules. We propose that these boundary sequences are foci of genetic recombination that serve to assort the modules and make the metabolic domain highly mosaic genetically

  8. Bacteriophage T4 multiplication in an Escherichia coli biofi