From aceska@victoria.tc.ca Fri Apr 1 15:40:35 2005 From: aceska@victoria.tc.ca (Adolf Ceska) Date: Fri, 1 Apr 2005 07:40:35 -0800 Subject: [BEN-L]BEN # CCCXLVI Message-ID: <000d01c536d1$2932d870$0828b440@HPLAPTOP001> BBBBB EEEEEE NN N ISSN 1188-603X BB B EE NNN N BBBBB EEEEE NN N N BOTANICAL BB B EE NN NN ELECTRONIC BBBBB EEEEEE NN N NEWS No. CCCXLVI April 1, 2005 aceska@telus.net Victoria, B.C. ----------------------------------------------------------- Dr. A. Ceska, P.O.Box 8546, Victoria, B.C. Canada V8W 3S2 ----------------------------------------------------------- ONE MUST AVOID THEORIES ALTOGETHER FOREIGN TO ORTHODOXY From: Nicolaus Copernicus to Pope Paul III - 1543 [The book _De Revolutionibus_ which was introduced by this dedication laid the foundations of modern astronomy.] I can easily conceive, most Holy Father, that as soon as some people learn that in this books which I have written concerning the revolution of heavenly bodies, I ascribed certain motions to the Earth, they will cry out at once that I and my theory should be rejected. For I am not so much in love with my conclusions as not to weigh what others will think about them, and although I know that the meditations of a philosopher are far more removed from the the judgment of the laity, because his endeavor is to seek out the truth in all things, so far as this is permitted by God to the human reason, I still believe that one must avoid theories altogether foreign to orthodoxy. Accordingly, when I considered in my own mind how absurd performance it must seem to those who know that the judgment of many centuries has approved the view that the Earth remains fixed as a center in the midst of the heavens, if I should, on the contrary, assert that the Erath moves; I was for a long time at a loss to know whether I should publish the commentaries which have written in proof of its motion, of whether it were not better to follow the example if the Pythagoreans and of some others, who were accustomed to transmit the secrets of Philosophy not in writing but orally, and only to their relatives and friends, as the letter from Lysis to Hipparchus bears witness. [...] Therefore, when I considered this carefully, the contempt which I had to fear because of the novelty and apparent absurdity of my view, nearly induced me to abandon utterly the work I had begun. A WHIFF OF SCANDAL From: St. Petersburg Times, Florida, November 2, 2003 http://www.sptimes.com/2003/11/02/Tampabay/A_whiff_of_scandal.shtml Each year more than 160,000 people stroll through Marie Selby Botanical Gardens and are dazzled by its spectacular orchid collection, from showy Cattleyas to delicate Paphiopedilums. But the most important orchid in Selby Gardens' history is not on display. It's the one that could wreck the place. When orchid collector Michael Kovach first spotted it at a roadside stand in Peru, he knew he had never seen anything like it: a tall stalk topped with a bloom as big as a man's hand, its petals a hot pink shading into deep purple. As Kovach carried that dazzling flower into a roomful of Selby Gardens' scientists in June 2002, he was greeted by "a simultaneous wave of eye-widening and mouth opening," Kovach wrote in an orchid-collector newsletter. Selby's staff moved quickly to lay claim to the honor of naming the new orchid. Working around the clock, they cranked out a scientific description and published it in a special edition of Selby's own journal. At Kovach's request, they named the plant after him: _Phragmipedium kovachii_. The announcement, hailed as one of the biggest orchid discoveries in 100 years, garnered international acclaim for the 13-acre institution on Sarasota Bay. Making the triumph even sweeter was the fact that Selby had beaten into print a rival orchid expert who was on the verge of publishing his own scientific description of the new species. But the taste of triumph soured. Peruvian officials lodged a formal complaint. Two months after he walked into Selby Gardens with the orchid, Kovach's greenhouse in Virginia was raided by federal agents. They rooted through Selby Gardens' records, too. A federal grand jury in Tampa has subpoenaed a dozen Selby employees and board members. As the yearlong investigation draws to a close, Selby is likely to be charged with violating laws designed to protect endangered plants from poachers. Selby's staff believes prosecutors will make an example of them to placate Peru, said Selby's crisis management consultant, Jeffrey Tucker. A criminal conviction could bring large fines and the loss of hundreds of thousands of dollars in grant money. Individuals could even face jail time. Attorneys' fees already are squeezing the garden's $3.2-million budget. "It's a real mess," said Paul Martin Brown, author of Wild Orchids of Florida. "It tarnishes Selby's reputation." The orchid scandal has so exacerbated tension among Selby's leadership that the executive director and eight board members have resigned. Furious donors are withholding contributions. Selby officials are "all kind of shocked at how they got into the middle of this," Tucker said. They had nothing but the best of intentions, he said. To Eric Christenson, the rival beaten by Selby, none of this is surprising. He says Selby's staff should never have let Kovach in the door. "These people are idiots," he said. "Everyone involved knew it was illegal." How could so much trouble stem from a single flower? To Lee Moore the answer is obvious. A veteran orchid collector whose business cards identify him as "The Adventurer," Moore advised Kovach in Peru. He says Kovach's craving for fame overrode concerns about legalities. "Oh, the cost of fame," said Moore, chuckling. Kovach (pronounced KO-vack), 48, lives in rural Virginia. Once a carpenter, he says God led him to the orchid business. It was a heavenly calling into a hellish obsession. While most orchid fanciers are content with the selection at Home Depot, a few are willing to blow $10,000 on one plant or brave any hardship to discover a new species. Orchid Fever author Eric Hansen blames the flowers' sensual form. The tumescent blooms and intoxicating scent can cloud a collector's judgment. Driven by passion, some orchid fanciers would spend their last dime for a flower such as the one Kovach found. "When a man falls in love with orchids, he'll do anything to possess the one he wants," Norman McDonald wrote in his 1939 book The Orchid Hunters. "It's like chasing a green-eyed woman or taking cocaine, it's a sort of madness." But such madness may run afoul of the law. Wild orchids are protected by an international treaty called the Convention on International Trade in Endangered Species. It prohibits collecting endangered plants in the wild for export. Trade is permitted only if the exporting country certifies the plants were grown in a nursery or laboratory. Few orchid experts like the treaty's rules, Brown said, and some would like to get rid of them. Thousands of orchids can be destroyed by a new road but collecting a few for scientific study can be nearly impossible. One orchid expert, Guido Braeme, punched out a customs official who accused him of smuggling. Still, Braeme was fined because he had no export permit for an orchid preserved in alcohol since 1822. According to Braeme, the rules are particularly maddening when the orchid is newly discovered. To get a permit to export it for study requires listing a name, but at that point there is no name. "You smuggle or you cheat," Braeme explained. "Legally you can't win." Still, botanical gardens continue to describe new species from other countries, Braeme said, suggesting they were all "based on illegal plants." Christenson, Kovach's rival who used to work for Selby, says he quit when he was ordered to write a grant proposal for propagating an illegally obtained orchid. "Everyone treats it with a kind of a nudge-nudge, wink- wink," Christenson said. "This is what all botanical gardens are doing." Selby's own rules require permits for plants shipped to its Orchid Identification Center. But so many orchids are sent to Selby "the Gardens does not require the submitters to provide documentation as to the sources of the plants," center director Wesley Higgins wrote last year. Moore says in all his years of shipping orchids to Selby, "nobody ever said boo about permits." So Moore says he advised Kovach to put his orchid in a suitcase and head for Selby without a permit. "I know he's supposed to have a permit . . . and he knows that very well, too," Moore said. But Moore said he told Kovach: "Take the (expletive) thing up there to Selby. If you try for a permit, you'll never get a permit." Moore has spent 25 years traipsing around South American jungles, collecting pre-Columbian art and new orchid species. Several are named for him. In _The Orchid Thief_, author Susan Orlean quotes Moore's Peruvian wife, Chady, as saying, "We were always smuggling something ... We had more going on, more situations than Indiana Jones! Oh, my God!" The Moores live in Miami but are building a nursery near the Peruvian city of Moyobamba. In 1996, flying back to Miami, Moore met Kovach. They started talking orchids and friendship blossomed. "He told me once, 'Lee, you're famous because you've got a lot of plants named for you. I wish I could have a plant named for me,' " Moore recalled. Last year, they agreed to rendezvous in Peru. In an orchid- collector newsletter published this summer, Kovach wrote that he went there to "discuss setting up a species production facility," using the Moores' nursery. He said they cut a deal. Moore denies it. On May 26, 2002, Kovach hired the Moores' driver to take him orchid hunting. About 3:30 p.m., Kovach wrote, they stopped at a place the map called El Progresso, actually just a truck stop. Farmers were selling orchids in the parking lot. Kovach picked out a few from a young brother and sister. The woman offered to fetch some special plants from behind the building. "She then quickly reappeared cradling three pots containing plants with large dark rose flowers," Kovach wrote. "They appeared to be slipper orchids of some kind, but I'd never seen anything like this." Kovach says he bought all three for $3.60 each. When Kovach showed them to his mentor later, Moore was stunned at their beauty. He remembered Kovach's hankering to have an orchid named after him. He says he told Kovach, "This is your chance. You've got the Holy Grail of orchids." In the Garden of Eden, Adam named everything. These days it's more complicated. There are strict rules on publishing new scientific names, and only certain taxonomists can do the naming. The American Orchid Society's list of approved taxonomists consists of just 23 experts, none in Peru. Last year, five were affiliated with Selby, more than any other botanical garden. Selby's experts knew about the orchid before Kovach arrived on June 5, 2002. A Texas grower had e-mailed them photos he had seen. They had also heard that Christenson had penned a description for _Orchids_ magazine, to be published June 17. Kovach wrote that Higgins, the center director, told him "a race for access to the plant had developed. He said it looked like I had won that race." As a result, Selby beat Christenson into print by five days. Christenson had wanted to name the new orchid _Phragmipedium peruvianum_ as a salute to Peru. He based his description on photos that had been e-mailed to him by a Peruvian nursery owner, because all ladyslipper orchids are on a most-endangered list. "Anyone with half a brain cell doesn't go near them," Christenson said. "They're the pandas of the orchid world. . . . When somebody shows up with an orchid like that, you either quietly tell them to go away or you call the cops." Selby's experts did neither. Kovach's newsletter account makes no mention of anyone asking him for permits. But in a December 2002 letter to federal authorities, Selby's attorney wrote: "Kovach advised Selby Gardens staff that he had legally imported the orchid into the United States and subsequently provided Selby Gardens with certain USDA permits and Peruvian certificates to support them." After Selby's scientists accepted Kovach's flower they asked him what to call it, and he told them to use his name. "I thought, well why not? I've worked long and hard; it can't hurt," Kovach wrote. Christenson says naming it kovachii was tantamount to saying, "Hey, come arrest me!" Three months later U.S. Fish and Wildlife Service officers raided Kovach's greenhouse. Then they hit Selby with a grand jury subpoena. Kovach contends he didn't need a permit because he wasn't transporting the orchid for commercial purposes, an argument experts don't buy. "His claim is nonsense," said Ned Nash of the American Orchid Society. Selby's legal problems are more complicated. Kovach left the orchid at Selby Gardens. After Selby's scientists finished, they shipped it to a museum in Peru without a permit. "In the strictest sense of the word, they broke the law," Nash said. They also did not send back the entire plant. As the scientists stood around Kovach's orchid "it began striking everyone that this was the last they were going to see of this," said Tucker, Selby's consultant. "It was taken from a high altitude in Peru and it was not going to survive in Sarasota. And someone said, "Why kill the last condor?' " So one Selby expert, John Atwood, took a piece to his home in Vermont to see if it would grow, Tucker said. Federal officials have now confiscated it. Selby officials were caught off guard by the investigation. Then-director Meg Lowman, a rain forest biologist who wrote a critically acclaimed memoir called _Life in the Trees_, was not even in town when Kovach showed up with his orchid. But she became the orchid's first casualty. For two years Lowman was the target of repeated sniping from Selby's chairman, a prominent orchid grower named Bob Scully who four years ago was banned from Selby's greenhouses over complaints of sexual harassment and other problems. According to Lowman's attorney, Robert Rivas, Scully was informed by Selby's experts about Kovach's orchid the day after it arrived, and he "enthusiastically endorsed" rushing the news into print, even meeting with the orchid experts to discuss it. When Selby's board learned of the federal investigation, board members asked Scully to deal with it, said former board member Bob Richardson. "We were always hopeful this thing was going to blow away," Richardson said. "It just kept escalating as time went on." Tension among board members escalated, too. For Richardson, the last straw came when "we were sitting in a meeting with the board and Scully was saying he thought Meg hadn't told the truth about what happened." Richardson quit. He had pledged $100,000 to Selby, but plans to give it to Lowman for her legal defense. Then Lowman was forced out, along with board members who supported her. Several have vowed to withhold donations worth hundreds of thousands of dollars. In Peru, the government posted fliers in the airports warning against smuggling the new orchid. But collectors stripped the site where Kovach's three plants came from, and the plants are selling for $1,000 each in Europe, said Harold Koopowitz, editor of Orchid Digest. Five months ago, though, Koopowitz saw 1,000 more growing on a remote cliff in the Andes. Their best protection is their location. Getting to them, Koopowitz wrote, required making what he called "the hike from hell." One person who hopes to profit from this is The Adventurer. When Kovach flew to Selby he left two of his orchids with Moore, who later paid local farmers to gather about 200 more for his nursery. The Moores now await the day when trade in them will be legal and lucrative. Most people connected to the case declined to comment. Kovach, who initially was talking to the New York Times, Washington Post and People, now refuses all interview requests as he awaits the grand jury's decision. "My life is ruined," he told People. "The bottom line is, it's just a flower. Everybody's lost their mind." [Post Scriptum: Selby had to take out a full-page ad in an orchid magazine apologizing for its role in the case. And Selby officials had to write to the international body in charge of scientific names for species, urging that Kovach's name be taken off the orchid.] HOMAGE TO A GOVERMNET From: Philip Larkin, _High Windows_. Next year we are to bring the soldiers home For lack of money, and it is all right. Places they guarded, or kept orderly, Must guard themselves, and keep themselves orderly. We want the money for ourselves at home Instead of working. And this is all right. It's hard to say who wanted it to happen, But now it's been decided nobody minds. The places are a long way off, not here, Which is all right, and from what we hear The soldiers there only made trouble happen. Next year we shall be easier in our minds. Next year we shall be living in a country That brought its soldiers home for lack of money. The statues will be standing in the same Tree-muffled squares, and look nearly the same. Our children will not know it's a different country. All we can hope to leave them now is money. [1974] ________________________________________________________________ Subscriptions: http://victoria.tc.ca/mailman/listinfo/ben-l Send submissions to aceska@telus.net BEN is archived at http://www.ou.edu/cas/botany-micro/ben/ ________________________________________________________________ From aceska@victoria.tc.ca Mon Apr 18 20:52:55 2005 From: aceska@victoria.tc.ca (Adolf Ceska) Date: Mon, 18 Apr 2005 12:52:55 -0700 Subject: [BEN-L]BEN # 347 - PART 1 Message-ID: <001a01c54450$3fa57e50$0828b440@HPLAPTOP001> This is a multi-part message in MIME format. ------=_NextPart_000_001B_01C54415.934B3A30 Content-Type: text/plain; charset="iso-8859-2" Content-Transfer-Encoding: quoted-printable =20 BBBBB EEEEEE NN N ISSN 1188-603X BB B EE NNN N =20 BBBBB EEEEE NN N N BOTANICAL BB B EE NN NN ELECTRONIC BBBBB EEEEEE NN N NEWS No. 347 April 15, 2005 aceska@telus.net Victoria, B.C. ----------------------------------------------------------- Dr. A. Ceska, P.O.Box 8546, Victoria, B.C. Canada V8W 3S2 ----------------------------------------------------------- BOTANY BC 2005 - REMINDER From: Elizabeth Easton [Elizabeth.Easton@gems3.gov.bc.ca] Botany BC 2005 will take place from Thursday May 26th through Sunday May 29th. Lytton will be the home base with field trips to the Stein and Botanie Valleys and the Skwaha Lake Ecological Reserve. The Program and Registration are available on the Botany BC website at: http://members.shaw.ca/dmeidinger/botanybc/ FUNGI - COMMON, RARE AND IN BETWEEN From: Bryce Kendrick, Mycologue Consultants, 8727 Lochside Drive, Sidney-by-the-Sea, B.C., V8L 1M8, Canada [bryce@mycolog.com] URL: www.mycolog.com Introduction Presumably, everyone has some idea of what he or she means when they use these words. Surely, you may say, a common fungus is one we encounter often, and a rare fungus is one we find only occasionally (or may never have seen). But in saying this we are merely moving the argument back a level. What do we mean by 'often', and 'occasionally'? 'Never' is unambiguous for any particular study, but proving actual total absence (as would be the case in extirpation or extinction) is extremely difficult. Certainly, we can all think of macrofungi we consider rare. I have seen the stellar _Collybia racemosa_ on only a few occasions (How many other agarics bear visible anamorphs on their sexual fructifications?) I have found _Asterophora lycoperdoides_, which parasitizes other agarics, even less often, and I have encountered its congener, _Asterophora parasitica_, only once or twice (Too bad, since these are amazing species in which the tissue of the mushroom cap becomes converted into asexual chlamydospores). At the other extreme, _Stropharia ambigua_ and _Pluteus cervinus_ are seen in the woodlands near my home on a regular annual basis, as is _Russula brevipes_. This raises the issue of geographical distribution. Some species which I remember as being 'common' in Ontario are not found at all on the west coast (and vice versa). That is a valid biogeographical issue, but it is beyond the scope of this essay. Here are a few other variables and factors not yet fully considered in studies of fungal occurrence in restricted areas: Distribution. Of course, even at the local level, we can only expect a fungus to occur in the appropriate habitat. Ectomycorrhizal mushrooms can be anticipated only where their host trees flourish. Saprobic fungi may be more widely distributed, though some of them, such as _Strobilurus trullisatus_, which grows almost exclusively on decaying Douglas fir cones, are highly substrate- specific. This essay does not deal with that aspect of mushroom distribution. The assumption being made is that we are seeking the fungi in their normal haunts. Fruiting season. The same kind of caveat applies to seasonality. No point in looking for most mushrooms in August along the east coast of southern Vancouver Island - it is simply too dry. So we must assume that the sampling is done at appropriate times of year. Size of individual fruit bodies. The size of a mushroom may also be expected to have some impact on the number of basidiomata produced. For example, we are unlikely to find as many fruit bodies of _Russula brevipes_, a very large agaric with caps 80-200 mm in diameter, as of _Mycena aurantiidisca_, the caps of which are usually only about 10 mm wide, since the biomass of an individual basidioma of the former must be several hundred times that of the latter, therefore representing a much larger investment of energy on the part of the mycelium (though we may note that the _Russula_ obtains most of its energy directly from a cooperative tree, while the _Mycena_ must depend on its own enzymes to degrade tree litter into an assimilable form.) Longevity. Not only the size, but also the longevity or persistence of fruit bodies will have an influence on the frequency with which they are recorded. There is some information on this, but it has yet to be compiled and consolidated, let alone factored into the equation that apparently needs to be attached to each taxon in this kind of study. Egli et al. (1997) found that monthly surveys recorded 31 per cent fewer taxa than weekly surveys. This reduction clearly springs from the differential longevity of fruit bodies in different species. Observer acuity. The size of basidiomata may also affect the likelihood of their being recorded. While _Russula brevipes_ is hard to miss, tiny grey or brown _Mycena_ species, unless present in numbers, can easily be overlooked, and there are much smaller 'macrofungi' out there as well. Nevertheless, I have assumed that, for the purposes of the various studies quoted here, experienced eyes will miss very little. Biological associations. It is clear that ectomycorrhizal fungi such as species of _Russula_ persist for years or generations on and around the roots of their plant partners. This makes it obvious that in years when such fungi do not fruit they are not absent from the habitat. Nevertheless we must be allowed to make at least some judgments about rarity on the basis of what we find fruiting, and the prolonged reluctance or inability of many fungi to make fruiting bodies on an annual basis would seem to affect their potential for long-distance dispersal. In light of the vehicle in which this essay is published, let me draw some perhaps instructive comparisons with plants. When looking for a plant, we can in many cases say that if after prolonged and extensive searching, we find it only in a few locations, it is rare. This will certainly be true of persistent plants such as trees or perennials. We cannot say exactly the same about ephemeral plants such as some small spring annuals which, if not sought at the proper time, will simply not be found. A majority of fungal fruit bodies are similarly fugacious, and will not be found unless sought during their evolutionarily determined fruiting season. There is one important difference between ephemeral plants and fungi. The plants often persist only as seeds, while in many cases the fungi live on as hidden, though extensive, mycelia, which can now be detected by molecular techniques. It is far easier to see and identify the fruiting part of the life cycle, when it occurs. Nevertheless, molecular approaches may ultimately revolutionize our concepts of rarity, though that potential revolution still lies in the future. Now we have clarified the conditions under which we are operating, we can proceed with the aim of the exercise, to devise useful (because partially quantified) definitions of '_common_', '_rare_', and intermediate categories, as they apply to fungi. This may help us in communicating about our collections, and may yield one or two generalizations about these matters. Fortunately, I am aware of some publications and databases which can be examined, and this paper will undertake a limited meta-analysis of these data, as well as of some unpublished data I have been involved in gathering. There may be many different ways of defining common vs. rare in a quantitative manner, but I will concentrate on only two. The first method, on which we have the most data, is based on the frequency of occurrence of fungal fruiting bodies over a period of several to many years. It does not consider the numbers of basidiomata found in any single year, but simply whether a fungus has been recorded in a particular year (that is the only information available from most such studies). The second method considers the numbers of fruiting bodies encountered in a single excursion or season, and although detailed studies in Japan have followed the occurrence of Matsutake basidiomata over many years, few if any such studies have apparently been carried out on an all-taxa basis. Method 1 - Extended linear studies One thing that becomes apparent as soon as we begin to analyse the available multi-year databases is that although they can give us a handle of sorts on the matter at hand, their extended duration, although far beyond that possible in most grant- supported studies, is nevertheless not long enough to ensure a full accounting of all the fungi that have the capacity to produce fruiting bodies in the various study locations. I'll begin by providing a few numbers from a study in which I was involved: a five-year macrofungal survey of Clayoquot Sound (Roberts et al. 2004). We recorded a total of 551 species, but only 28 were found in all years, and 310 were seen in only one year. On average we found over 100 newly encountered taxa each year. Although the study lasted for only 5 years, the results already suggest: 1. that there are few common fruiting macrofungi; 2. there are many rarely or occasionally fruiting fungi; and 3. there is an ongoing influx of previously unrecorded taxa to the database. These numbers - the continuing high level of novelty we encountered - led us to assume that this accretion of taxa could be expected to continue for many years. Other longer-term studies confirm this impression. A fascinating study by Tofts and Orton (1998) points out that although they had collected agarics regularly in a particular woodland in Scotland for 21 years, and had recorded 502 species in that time, in each successive year they still found species they had never seen before. They collected for over twenty years, and still could not say that they had a proper handle on agaric biodiversity in that woodland. They suggested that at least 25 to 30 years of collecting, and possibly more, would be necessary before that goal could be attained. I think they were being conservative in this estimate. It also seems intuitively obvious that fungi which appear only after more than two decades must be regarded as rare, at least by some definitions. Yet it is entirely possible that such laggards will be locally abundant when, eventually, they do fruit (see method 2). A more recent paper by Straatsma et al. (2001) emphasizes many of the same points. They collected basidiomata weekly for 21 years (1975-1979, and 1984-1999), and recorded over 400 species in a 1500 m2 plot. Yet only 8 (eight) species (2 per cent) were found every year. The number of species found per year ranged widely - from 18 to 194 - and even in the last year of the study, 19 species appeared which had not previously been found. Clearly, the authors had not seen the full diversity of macrofungi that existed in their plot. Significantly, 37 per cent of the taxa they recorded were found in only one year. In Fall 2003 the Cascade Mycological Society held its 16th successive mushroom fair at the Mount Pisgah Arboretum just outside Eugene, Oregon. As a guest speaker for the Society I was fortunate enough to be invited to participate in the collecting trips leading up to the fair. The fair is an exciting survey of the larger fungi because over 300 species are usually on display - bespeaking a huge effort on the part of many members. I was also fortunate enough to get my hands on the statistics for all sixteen years. Over those years almost 700 species have been recorded from the extensive and diverse habitats sampled by C.M.S. collectors. When we arranged the data according to the number of years in which each species had been collected, an interesting picture emerged. Let us begin with the extremes. Only 37 species (5.5 per cent per cent of the total number) had been found in all sixteen years. Equally thought-provoking was the fact that no fewer than 190 species (almost 30 per cent of the total) had been recorded only once in those 16 years, and almost one hundred more (nearly 14 per cent) in only two of the 16 years. Here is the list of species versus years recorded. Species Years recorded % of total species 37 16 5.5 44 15 6.5=20 31 14 4.6 24 13 3.6 13 11 1.9 20 12 3.0=20 18 10 2.7 18 9 2.7 22 8 3.3 22 7 3.3 22 6 3.3 41 5 6.1 29 4 4.3 48 3 7.1 92 2 13.7 190 1 28.3 =20 There are possible flaws in the data set. For example, some species may have been misidentified. But the general trends are obvious. A relatively small number of taxa will show up every year, or almost every year, while a larger number of taxa will be found much less often, and a very large number will be encountered only once every decade or so. How many more taxa will show up in the years to come? What is the full number of species that the Cascade group can expect to find if they keep at it long enough? If we may be allowed to take a quick look in the crystal ball, might we not forecast that after 50 years they will have found 1,000 species fruiting? This data set (for which I am indebted to the hardworking collectors and record-keepers of the Cascade Mycological Society) points up the necessity for very long-term studies wherever the diversity of fungi is to be fully explored, and calls for the accumulation of much concurrent data on weather conditions and other ecological factors if we are to understand why some fungi are so notably reluctant to fruit. How are we to calculate common and rare in this case? It seems that we have no alternative but to make a few arbitrary decisions. For example, can a species be regarded as common if it does not occur every year? If we can countenance that concept, how many years of absence could be accepted for a 'common' species? We must remember that seasons differ widely in the degree of encouragement they offer to the fruiting of mushrooms - too dry, too cold, even too wet, are well-known situations. So it might be necessary to temper our purely numerical concerns with an injection of weather data. However, I do not have that information for any of the linear studies, and must leave it to their authors to provide such input, if they see fit. My tentative, arbitrary, and open-to-debate conclusions from the linear Cascade Mycological Society study are as follows. 1. Ubiquitous or abundant: a fungus must occur in every year. Applies to about 5 per cent of taxa recorded in the Cascade Mycological Society database. 2. Common: a fungus must be recorded 4 years out of 5. Applies to just over 10 per cent of the taxa recorded in the C.M.S. database. 3. Sporadic or occasional: taxa recorded in 2 or 3 years out of 10. Applies to about 35 per cent of the taxa recorded by C.M.S. 4. Uncommon or infrequent: those taxa which occurred in only 1 year out of 5 or less often, down to 1 year in 10. Applies to about 20 per cent of the taxa recorded by C.M.S. 5. Rare: those taxa which occurred less often than 1 year in 10. This applies to almost 30 per cent of the taxa recorded by C.M.S. =20 To iterate: in the linear C.M.S. study: abundant - 5 per cent, common - 10 per cent, sporadic - 35 per cent, uncommon - 20 per cent, rare - 30 per cent. I believe that if the sampling is continued for another decade or more, the number of uncommon and rare fungi will increase substantially, producing a chart more closely resembling that emerging from the mould study reported below. This is a mathematical certainty, since no further abundant or common fungi could possibly emerge, while uncommon and rare fungi would continue to be added to the list. Method 2: Concurrent frequency of occurrence For the past two years I have been involved in several expeditions aimed at compiling a macrofungal inventory of the islands of Gwaii Haanas National Park Reserve in the Queen Charlotte archipelago (Haida Gwaii), British Columbia, Canada. During the expedition of Fall 2004 I undertook to record the numbers of fruit bodies of every taxon we encountered on the various islands. Over a period of 9 days I recorded well over 4,500 fruit bodies found by our 4- person team. We recorded 161 taxa, the numbers of specimens ranging from 1 to well in excess of 100 - I simply stopped counting when we exceeded 100 fruit bodies on any given foray. Of the 161 taxa, 53 were represented by a single fruit body, while 14 species considerably exceeded the 100 mark. Between those extremes there were 13 species with 2 fruit bodies each, 8 species with 3 fruit bodies, 10 species with 4, 9 species with 5, 6 species with 6, 19 species with between 10 and 19, 14 species with between 22 and 45, 5 species with between 59 and 66. So there was a concentration of taxa at the lower and upper ends of the scale, with very low numbers in between. If we accept fewer than 10 fruit bodies as indicating a degree of scarcity, this distribution suggests that 109 of the 161 taxa - almost 68 per cent - are uncommon. If we accept the discovery of 50 or more fruit bodies as indicating a common species, there were 19 such species, or 12 per cent of the total. The other 20 per cent lay somewhere between those extremes. It is also apparent that the 14 species (8.7 per cent of the total taxa) of which more than 100 specimens were seen (in several cases many more than 100) represent approximately 50 per cent of all fruit bodies encountered in the survey. That seems to me to be an incontrovertible measure of commonness. =20 My suggestions for ranking our data are as follows: 1. Abundant: represented by over 100 fruit bodies: just under 9 per cent of Gwaii Haanas taxa. 2. Common: represented by 59-66 specimens: 3 per cent of Gwaii Haanas taxa. 3. Sporadic or scattered: represented by 10-44 fruit bodies: 20 per cent of Gwaii Haanas taxa. 4. Uncommon: represented by 2-9 fruit bodies: 34 per cent of Gwaii Haanas taxa. 5. Rare: represented by a single collection: 33 per cent of Gwaii Haanas taxa. =20 To iterate: in the concurrent Gwaii Haanas study: abundant - 9 per cent, common - 3 per cent, sporadic - 20 per cent, uncommon - 34 per cent, rare - 33 per cent. Before continuing I must state a number of reservations about our data. 1. Sometimes 20 (or even 100) specimens would be accumulated gradually, found scattered in many different places. Sometimes the same number would be found together in one narrowly circumscribed area. In this case the numbers are misleading. What is needed is a more fine- grain method of recording the data, and I will apply one on our next survey, perhaps recording fungi as scattered or localized (or solitary or aggregated). 2. Some method of comparing biomass is called for (_Mycena_, for example, being generally minute, and _Russula_ comparatively massive) and I will attempt to implement one in our next survey. I hope that other surveys of this kind will be done, perhaps on a larger scale, perhaps repetitively over a longer period, so that the kind of information we can derive from them will be placed on a sounder statistical basis. Our study, carried out by boat over a limited period, was perforce more a snapshot than a total seasonal compilation. It would be interesting to examine the results of, for example, a weekly sampling over an entire season, to see how the grouping of taxa might change. This would be impossibly expensive in Gwaii Haanas, but could certainly be done elsewhere. I realize that it is unwise to read too much into a single survey, but our study does seem to confirm that there is a large number of uncommon species, a larger group of intermediate occurrence, and a much smaller number of common species, which last provide the majority of all fruit bodies. However, I suspect that had the surveys been more intensive or extensive, we might well have found a much larger number of rare or uncommon taxa, making the chart look more like that produced in the mould study below. These results lead inescapably to a consideration of the manner in which identification keys should be constructed. It seems to me that such keys, especially when dichotomous, and when designed for amateurs, should concentrate on the common species, and should imply that taxa not covered are probably rare and should be left to the experts. This would mean that such selective keys would be shorter and simpler, and therefore have a greater chance of conferring success on the user. Although the species that are common in one geographic location will be different from those seen in another area, keys can be compiled either with a specific area (such as those produced by the Pacific North West Key Council) or particular habitats in mind, or, if wider ranging, will still deal with fewer taxa than the usual dichotomous keys encountered in the various manuals. By reducing the number of dichotomies, this simple strategy could prevent much frustration on the part of users, and would make such keys more accessible. Fungi on indoor substrates. A database (Thiagarajan et al. 2004) of 167 fungal taxa recorded on various indoor substrates during 76,000 examinations of various kinds of samples (bulk, tape and swab) shows that there are only a few really common fungi in this environment. 3 taxa were found in more than 10 per cent of samples 6 taxa occurred in between 10 per cent and 1 per cent of samples 34 taxa occurred in between 1 per cent and 0.1 per cent of samples 52 taxa occurred in between 0.1 per cent and 0.01 per cent of samples 72 taxa occurred in between 0.01 per cent and 0.001 per cent of samples It is interesting to note that of the 167 taxa noted here, 124 were hyphomycetes, 20 ascomycetes (including 2 of the top 10), 9 zygomycetes, 4 basidiomycetes, 4 coelomycetes, 3 myxomycetes (protozoans rather than fungi), 2 yeasts and 1 oomycete (a chromistan fungus). My arbitrary suggestion, having examined these data, is that we regard the three taxa with more than 10 per cent frequency of occurrence as abundant, those between 10 per cent and 1 per cent as common, those with between 1 per cent per cent and 0.1 per cent as sporadic, those between 0.1 per cent per cent and 0.01 per cent as uncommon, and those below 0.01 per cent per centas rare. =20 This arrangement has no persuasive statistical underpinning, but it looks as if, no matter what scheme of partitioning was to be adopted, a similar pattern would emerge, sooner or later. The more samples one examined, the more collecting trips one took, the more years a study endured, the more likely seems this last kind of bar chart. So this is the generalization that seems to emerge from this analysis. Not a surprise to many of us, but, given the profusion of mushrooms that emerged in Fall of 2004 on the west coast of North America, not something that stared us in the face as we forayed so successfully. Conclusions 1. Most fungi are rare (at least in the sporulating condition), and very few can be regarded as common, at least by the criteria used in many kinds of sampling programs. (Of course, I must also mention the contrarian view, which is that there are actually few rare fungi, and that we just don't know how to find them, or that there are so few mycologists in many areas of the world that many fungi will not even be recorded, even when they occur in large numbers). There is also the real possibility that many fungi exist for long periods, or even permanently, without sporulating. This avenue will undoubtedly be explored in the relatively near future by means of PCR-DNA techniques, but for the present we tend to assume that most fungi sporulate, even if only sporadically, as a requirement for success and dispersal. Certainly moulds, which constitute the major part of the spectrum explored in the indoor substrate study documented above, will not have access to newly available substrates unless their spores are in the air. 2. Keys for identification, if dichotomous, should be designed to arrive at common species first, and at truly rare species last (if at all). Of course, if keys are synoptic, this is not a consideration unless the inclusion of too many taxa introduces too many characters, or too much confusion or 'noise', to the identification process. Rarity is likely to increase as fungal habitats are destroyed by human agency. Red lists will become longer (if it is not too late to compile them - many species will not even get to be in a red list before they disappear). Those wishing to analyze the matter of rarity more deeply can find food for thought in fine papers by Stebbins (1980) and Fiedler and Ahouse (1992), though those essays were written from the botanical point of view. I would also like to cite a paper by Hawksworth (2004) in which he revisits the matter of the probable numbers of extant fungi as estimated from the number already found and described, and from the relative numbers of higher plants. It would appear that about 100,000 distinct taxa of fungi have been described, from an estimated total of about 1.5 million. It is significant in the context of the present document that we appear to have described only about 7 per cent of the fungi in existence. Hawksworth speculates that: (1) many of the missing fungi are in tropical forests; (2) many are in unexplored habitats; and (3) many are hidden in already described taxa: for example, the mould, _Fusarium graminearum_, formerly thought to be well- understood, is now known to comprise a complex of nine species. None of these caveats can disguise the fact that most of the 'missing' fungi are almost certainly rare. In conclusion, I want to share a few delightful lines from page 131 of Stephen Jay Gould's book 'The Flamingo's Smile' (1985) which might well be applicable to the present discussion. He is analyzing a much earlier paper by Lord Kelvin which purported to establish a (much too young) age for the Earth: 'Thus, although all three arguments had a quantitative patina,=20 none was precise. All depended upon simplifying assumptions=20 that Kelvin could not justify. All therefore yielded vague=20 estimates with large margins of error.' I would like to thank Adolf Ceska for invaluable input during the gestation of this piece. References Egli, S., F. Ayer, & F. Chatelain. 1997. Die Beschreibung der Diversit=E4t von Makromyzeten. Erfahrungen aus pilz=F5kologischen Langzeitstudien im Pilzreservat La Chan=E9az, FR. _Mycol. Helv._ 9: 19-32. Fiedler, P.L. & J.J. Ahouse. 1992. Hierarchies of cause: toward an understanding of rarity in vascular plant species. Pp. 23-47 in: Fiedler, P.L. & S.K. Jain (eds.) _Conservation Biology. The Theory and Practice of Nature Conservation, Preservation and Management._ Chapman and Hall, New York. 507 p. UVIC Library QH75 C662 Hawksworth, D.L. 2004. Fungal diversity and its implications for genetic resource collections. _Studies in Mycology_ 50: 9-18. Roberts, C., O. Ceska, P. Kroeger & B. Kendrick. 2004. Macrofungi of Six Habitats over Five Years in Clayoquot Sound, Vancouver Island. _Can. J. Bot._ 82: 1518- 1538. Stebbins, G.L. 1980. Rarity of plant species: a synthetic viewpoint. _Rhodora_ 82: 77-86. Straatsma, G., F. Ayer, & S. Egli. 2001. Species richness, abundance, and phenology of fungal fruit bodies over 21 years in a Swiss forest plot. _Mycol. Res._ 105: 515-523. Thiagarajan, S., P. Fallah, H. Burge, & J. Gallup. 2004. _Cumulative index of fungi reported from various indoor substrates_. - Poster presentation, PAAA Annual Conference, San Diego, June 2004. Tofts, R.J. & Orton, P.D. 1998. The species accumulation curve for Agarics and Boleti from a Caledonian pinewood. _Mycologist_ 12: 98-102. 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AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAMATQBhAGkAbABTAHQAcgBlAGEAbQAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAYAAIA////////////////AAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAgAAAAwAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAD///////////// //8AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAP///////////////wAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAA////////////////AAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAAA AAAAAAAAAAAAAAAAAAAAAAAAAAAAAgECNwEAAAAAAAAAAwAFNwYAAAACAQo3AQAAAAsAAAAqhkiG 9xQDCgMCAQADAAs3blkAAAMAFDcAAAAAAwD6fwAAAABAAPt/AEDdo1dFswxAAPx/AEDdo1dFswwD AP1/AAAAAAsA/n8AAAAAAwAhDgUhJQACAfgPAQAAABAAAADAZwj1QANVTYmoMbZqiVPpAgH6DwEA AAAQAAAAwGcI9UADVU2JqDG2aolT6QMA/g8HAAAA+O0= ------=_NextPart_000_001B_01C54415.934B3A30-- From aceska@victoria.tc.ca Mon Apr 18 22:51:45 2005 From: aceska@victoria.tc.ca (Adolf Ceska) Date: Mon, 18 Apr 2005 14:51:45 -0700 Subject: [BEN-L]BEN # 347 - Part 2 Message-ID: <000401c54460$d50ebff0$0828b440@HPLAPTOP001> This is a multi-part message in MIME format. ------=_NextPart_000_0005_01C54426.28B90FB0 Content-Type: text/plain; charset="iso-8859-1" Content-Transfer-Encoding: quoted-printable =20 =20 RAUNKIAER'S RULE IN ECOLOGY AND EPIDEMIOLOGY From: J=E1nos Izs=E1k, Zoological Department, Berzsenyi College, Szombathely, Hungary [ijanos@bdtf.hu] based on Izs=E1k, J., C. Siffel, & A. Rosano. 2004. Validity of Raunkiaer's rule in epidemiology. _Central European Journal of Occupational and Environmental Medicine_ 10, 170-183. =20 The statistical phenomenon called Raunkiaer's rule is well-known to ecologists. According to this rule the distribution of species in occupancy (constancy, ubiquity) classes shows a characteristic form (Raunkiaer 1934, Preston 1948, Dahl 1956, McIntosh 1962, Collins and Glenn 1990; for further literature see e.g. Gotelli and Simberloff 1987, Hanski 1982, McGeoch and Gaston 2002).The number of species belonging to the lowest and the upper occupancy class or classes significantly exceeds the number of species in middle occupancy classes. An occupancy class [n,m] is here a frequency class of species. A species belongs to this frequency class, if it occurs in n or n+1 quadrats or similar units. The number of occupancy classes is usually chosen to be between five and ten. It is debatable whether the rule is basically biological or can be derived from formal statistical conditions. Data on the validity of the rule in other disciplines would support the latter hypothesis. =20 We carried out related investigations on epidemiological statistics. A formal analogy between ecological and epidemiological scenarios is straightforward. Species can be thought of as corresponding to diagnosis categories and individuals to established diagnoses. Sample quadrats or similar units can correspond e.g. to nearly equal sized counties of a state or to equal time intervals. Our investigations were also motivated by some of our previous work on the possible background of the rule. We found earlier that the truncated lognormal distribution fitted well numerous epidemiological data sets (Izs=E1k and Juh=E1sz- Nagy 1982). On the other hand, by using simulation method we found that the lognormal distribution of species abundances leads to a valid Raunkiaer' rule (Papp and Izs=E1k 1995). This is why we thought the rule would be valid in epidemiology and decided to test it. =20 The data were Hungarian statistics on infectious diseases and congenital anomalies at birth, both classified by counties and months. We established five classes for occupancies in the 19 counties (Table 1) and four for months (Table 2). =20 Occurrence Number of class counties in which the disease occurred I 1-4 II 5-8 III 9-12 IV 13-16 V 17-19 =20 Table 1. =20 Occurrence Number of class months in which the disease occurred I 1-3 II 4-6 III 7-9 IV 10-12 =20 Table 2. =20 The main results are the numbers of diagnosis categories falling into each occurrence class (Tables 3,4). The distribution in occupancy classes for counties is given in Table 3. =20 Infectious diseases Congenital anomalies at birth Occurrence 1984 1985 1991 2001 1990 1990- 1989- 1988- class 1991 1992 1993 I 8 9 11 14 54 50 33 29 II 5 3 1 5 24 22 31 26 III 0 2 4 4 12 15 17 21 IV 4 5 4 8 8 15 17 21 V 12 11 11 18 12 18 30 38 =20 Table 3. Number of diseases falling into the occurrence classes for counties. For example, figure 8 in 1984 refers to the fact that eight infectious diseases were reported in 1-4 =20 counties in that year. =20 The distribution in occupancy classes for months is given in Table 4. =20 =20 Infectious diseases Congenital anomalies at birth Occurrence class 1984 1985 1991 2001 1990 1990-1991 1989-1992 1988-1993 I 6 7 6 7 44 35 24 25 II 1 3 3 5 19 17 26 16 III 3 3 4 6 18 24 6 18 IV 19 17 18 31 29 44 72 76 =20 =20 =20 Note that the congenital anomalies data make it possible to imagine the change in shape of occurrence class vs. number of diagnoses graphs got by increasing the sample size, c.f. Gaston (1994). The numbers demonstrate unambiguously the validity of the rule in epidemiology. Of course, with very small or large total diagnosis numbers the rule would appear distorted. As mentioned above, the origin of the rule is probably the (nearly) lognormal distribution of the diagnosis frequencies. Indeed we found that the truncated lognormal distribution fitted the diagnosis frequencies well. Computations were carried out using the program package DIVERSI 2.1 (Izs k 2003), containing programs for fitting and diversity calculations and available at no cost by e- mail from the author. =20 A general conclusion is that analogous statistical conditions lead to similar statistical phenomena in remote scientific fields. For example, processes affecting plant species and infectious diseases (but not congenital diseases) show similar traits from a dynamical point of view. A remarkable link between these processes can be the data on the validity of Raunkiaer's rule for anthropochorous plants observed in isolated old houses and small villages, cited by Hanski(1982). At any rate, our findings are warning informations for researchers searching for ecological background of the rule. Naturally, possible ecological consequences of the rule and, in turn, the near- lognormal distribution, remains a question. =20 A note: not mentioned in the article, we have observed signs of latitudinal decline of virus diversity moving north in England (Hunter and Izs=E1k 1993). This finding can be another data arguing for a more wide occurrence of a phenomenon often mentioned in ecology. =20 Acknowledgement =20 I should express my gratitude to Professor Mark Williamson for his valuable remarks and numerous corrections in the text. =20 References =20 Collins, S.L. & S.M. Glenn, S.M. 1990. A hierarchical analysis of species' abundance patterns in grassland vegetation. _Amer. Nat._ 35: 633-648. Dahl, E. _Rondane: Mountain vegetation in south Norway and its relations to the environment._ I Kommisjon hos H. Aschehoug & Co. (W. Nygaard), Oslo. 374 p. Gotelli, N.J. & D. Simberloff. 1987. The distribution and abundance of tallgrass prairie plants: a test of the core- satellite hypothesis. _Amer. Nat._ 13:, 18-35. Hanski, I. 1982. Dynamics of regional distribution: the core and satellite species hypothesis. _Oikos_ 38: 210-221. Hunter, P.R. & J. Izs=E1k. 1993. A latitudinal diversity gradient in virus infections in humans in England and Wales. _Internat. J. Epidem._ 22: 144-148. Izs=E1k, J. 2003. DIVERSI 2.1: New version of a program package for calculating diversity and related statistics. _Community Ecol._ 4: 237-239. Izs=E1k, J. & P. Juh=E1sz-Nagy. 1982. Studies of lognormality on mortality statistics. _Biometr. J._ 24: 731-741. McGeoch, M.A. & K.J. Gaston. 2002. Occupancy frequency distributions: patterns, artefacts and mechanisms. _Biol. Rev._ 77: 311-331. McIntosh, R.P. 1962. Raunkiaer's law of frequency. _Ecology_ 43: 533-535. Papp, L. & J. Izs=E1k. 1995. Bimodality in occurrence classes: a direct consequence of lognormal distribution of abundances - a numerical experimentation. _Oikos_ 79: 191- 194. Preston, F.W. 1948. The commonnes, and rarity, of species. _Ecology_ 29: 254-283. Raunkiaer, C. 1934. The Life Forms of Plants and Statistical Plant Geography. _Collected Papers of C. Raunkiaer._ Clarendon Press, Oxford. =20 =20 BOOK REVIEW: LAND SNAILS (AND SLUGS) OF BRITISH COLUMBIA From: Julia Sigwart [julia.sigwart@ucd.ie] originally published in the American Malacological Society Newsletter vol. 36 (1) Spring 2005 Page 4 =20 Forsyth, Robert G. 2004. _Land Snails of British Columbia._ Royal British Columbia Museum Handbook, Royal British Columbia Museum, Victoria, BC, Canada. iv+188 p.=20 ISBN 0-7726-5218-X [soft cover] Price: CDN$25.95 + postage. Available in the USA from University of Washington Press, or e-mail shop@royalbcmuseum.ca =20 Local people in British Columbia often refer to two varieties=20 of slugs - "good" slugs, the native giant Banana Slug _Ariolimax columbianus_ and "bad" slugs, the invasive giant Black Slug _Arion_ spp. =20 In contrast, Land Snails of British Columbia covers the natural history of the entire terrestrial gastropod fauna including 92 species of snails and slugs. This book is the first comprehensive checklist and key to landsnails in western Canada, and clearly, it fills an important gap. I am personally impressed that Forsyth declines to cash in on the tremendous popularity of the Banana Slug (_Ariolimax columbianus_) and gives it only equal or less coverage than other species, many of which are very poorly studied. Every snail or slug has a one to two-page description including identification features, distribution and life history, and a selection of essential primary references. Forsyth uses contemporary classification based on recent work rather than relying on the classic Pilsbry definitions, but also includes common names for all taxa. The most attractive feature of the book is the identification key, for use in the field, presented in terminology that is precise (and impartial) but not intimidatingly technical. Copious black and white illustrations also help distinguish the animals. Since no gastropods are endemic to B.C., this publication will be of great use to all malacologists west of the Rocky Mountains. =20 The book is up to the high standards of the other Handbooks published by the Royal BC Museum, and a great addition to any natural history library. =20 [For Robert Forsyth's _Key to the slugs of British Columbia_ see BEN # 320, Dec 30, 2003. - AC] =20 =20 RE: A WHIFF OF SCANDAL (BEN # CCCXLVI) From: Toby Spribille [tspribi@gwdg.de] =20 Hi Adolf, =20 Your April Fool's BEN story on the Peruvian orchid must be the basis for a recent evening _Krimi_" I watched when I was too tired to sitting and looking at lichens. It was in the German evening _Krimi_ series _Tatort_, set at a huge, posh orchid show near Lake Konstanz, with a guy who recently described an illegally acquired red lady's slipper murdered in cold blood by a female orchid fanatic who claimed it was her right to describe. Like the Selby story, this was portrayed as the "orchid find of the century", though in this case from Vietnam. The customs inspector who was caught on the crime scene trying to steal the plant later confessed to selling exotic orchids illegally to an Oriental collector - two crimes nailed with one swipe. Remarkably, the orchid involved looked not unlike that on the St. Petersburg Times website, although it was much darker red. The type specimen, we were told, went to the herbarium at the University of Konstanz. I just found the episode online, under the name _Der Name der Orchidee_, at http://www.daserste.de/tatort/sendung.asp?datum=3D06.03.2005 =20 All the best, Toby =20 [_Der Name der Orchidee_ (SWR) Klara Blum (Eva Mattes) Sonntag, 6. M=84rz 2005 im Ersten "Alle jagen den roten Frauenschuh" Guess the Chief Botanist's name in this story! - His name was Dr. Klaus Raven! - AC] =20 ________________________________________________________________ =20 Subscriptions: http://victoria.tc.ca/mailman/listinfo/ben-l Send submissions to aceska@telus.net BEN is archived at http://www.ou.edu/cas/botany-micro/ben/ ________________________________________________________________ ------=_NextPart_000_0005_01C54426.28B90FB0 Content-Type: text/html; charset="iso-8859-1" Content-Transfer-Encoding: quoted-printable

 

 

RAUNKIAER'S RULE IN = ECOLOGY AND EPIDEMIOLOGY

From: = J=E1nos Izs=E1k,

=A0=A0 Zoological = Department,

=A0=A0 = Berzsenyi College,

=A0=A0 = Szombathely, Hungary

=A0=A0 = [ijanos@bdtf.hu]

=A0=A0 based = on

=A0=A0 = Izs=E1k, J., C. Siffel, & A. Rosano. 2004.

=A0=A0 Validity of = Raunkiaer's rule in

=A0=A0 = epidemiology. _Central European Journal of

=A0=A0 Occupational = and Environmental Medicine_ 10,

=A0=A0 = 170-183.

 

The statistical = phenomenon called

Raunkiaer's rule is well-known to

ecologists. = According to this rule the

distribution of = species in=A0 occupancy

(constancy, = ubiquity) classes shows a

characteristic form (Raunkiaer 1934,

Preston 1948, Dahl 1956, McIntosh 1962, Collins and

Glenn 1990; for = further literature see e.g.

Gotelli and = Simberloff 1987, Hanski 1982,

McGeoch and Gaston = 2002).The number of

species belonging = to the lowest and the

upper occupancy = class or classes

significantly = exceeds the number of species

in middle occupancy = classes. An occupancy

class [n,m] is here = a frequency class of

species. A species = belongs to this

frequency class,=A0 = if it occurs in n or n+1

quadrats or similar = units. The number of

occupancy classes = is usually chosen to be

between five and = ten. It is debatable

whether the rule is basically biological or

can be derived from = formal statistical

conditions. Data on = the validity of the

rule in other = disciplines would support the

latter = hypothesis.

 

We carried out = related investigations on

epidemiological = statistics. A formal

analogy between = ecological and

epidemiological = scenarios is

straightforward. = Species can be thought of

as corresponding to diagnosis categories

and individuals to established diagnoses.

Sample quadrats or = similar units can

correspond e.g. to = nearly equal sized

counties of a state = or to equal time

intervals. Our investigations were also

motivated by some = of our previous work on

the possible = background of the rule. We

found earlier that = the truncated lognormal

distribution fitted = well numerous

epidemiological = data sets (Izs=E1k and Juh=E1sz-

Nagy 1982). On the = other hand, by using

simulation method = we found that the

lognormal = distribution of species

abundances leads to = a valid Raunkiaer' rule

(Papp and = Izs=E1k 1995). This is why we

thought the rule = would be valid in

epidemiology and = decided to test it.

 

The data were = Hungarian statistics on

infectious diseases = and congenital

anomalies at birth, = both classified by

counties and = months. We established five

classes for = occupancies in the 19 counties

(Table 1) and four = for months (Table 2).

 

Occurrence Number = of

class=A0=A0=A0=A0=A0 counties in

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 which the

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 disease

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 occurred

I=A0=A0=A0=A0=A0=A0=A0=A0=A0 1-4

II=A0=A0=A0=A0=A0=A0=A0=A0 5-8

III=A0=A0=A0=A0=A0=A0=A0 9-12

IV=A0=A0=A0=A0=A0=A0=A0=A0 13-16

V=A0=A0=A0=A0=A0=A0=A0=A0=A0 17-19

 

Table = 1.

 

Occurrence Number = of

class=A0=A0=A0=A0=A0 months in

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 which the

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 disease

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 occurred

I=A0=A0=A0=A0=A0=A0=A0=A0=A0 1-3

II=A0=A0=A0=A0=A0=A0=A0=A0 4-6

III=A0=A0=A0=A0=A0=A0=A0 7-9

IV=A0=A0=A0=A0=A0=A0=A0=A0 10-12

 

Table = 2.

 

The main results = are the numbers of diagnosis categories falling

into each = occurrence class (Tables 3,4). The distribution in

occupancy classes = for counties is given in Table 3.

 

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 Infectious diseases=A0=A0=A0=A0=A0=A0 Congenital anomalies at

=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 = =A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0birth

Occurrence 1984=A0 = 1985=A0=A0 1991=A0=A0 2001=A0 1990 1990-=A0=A0 1989-=A0=A0 1988-

class=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0= =A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0 1991=A0=A0=A0 1992=A0=A0=A0 1993

I=A0=A0=A0=A0=A0=A0=A0=A0=A0 8=A0=A0=A0=A0 9=A0=A0=A0=A0=A0 11=A0=A0=A0=A0 14=A0=A0=A0 54=A0=A0 50=A0=A0=A0=A0=A0 33=A0=A0=A0=A0=A0 = 29

II=A0=A0=A0=A0=A0=A0=A0=A0 5=A0=A0=A0=A0 3=A0=A0=A0=A0=A0 1=A0=A0=A0=A0=A0 5=A0=A0=A0=A0 24=A0 =A022=A0=A0=A0=A0=A0 = 31=A0=A0=A0=A0=A0 26

III=A0=A0=A0=A0=A0=A0=A0 0=A0=A0=A0=A0 2=A0=A0=A0=A0=A0 4=A0=A0=A0=A0=A0 4=A0=A0=A0=A0 12=A0=A0 15=A0=A0=A0=A0=A0 = 17=A0=A0=A0=A0=A0 21

IV=A0=A0=A0=A0=A0=A0=A0=A0 4=A0=A0=A0=A0 5=A0=A0=A0=A0=A0 4=A0=A0=A0=A0=A0 8=A0=A0=A0=A0 8=A0=A0=A0 15=A0=A0=A0=A0=A0 = 17=A0=A0=A0=A0=A0 21

V=A0=A0=A0=A0=A0=A0=A0=A0=A0 12=A0=A0=A0 11=A0=A0=A0=A0 11=A0=A0=A0=A0 18=A0=A0=A0 12=A0=A0 18=A0=A0=A0=A0=A0 30=A0=A0=A0=A0=A0 = 38

 

Table 3. Number of = diseases falling into the occurrence

classes for counties. For example, figure 8 in 1984 refers to

the fact that eight infectious diseases were reported in = 1-4=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0=A0

counties in that year.

 

The distribution in occupancy classes for months is given in

Table = 4.

 

 

Infectious diseases

Congenital anomalies at birth

Occurrence class

1984=

1985=

1991=

2001=

1990=

1990-1991

1989-1992

1988-1993

I

6

7

6

7

44

35

24

25

II

1

3

3

5

19

17

26

16

III<= /font>

3

3

4

6

18

24

6

18

IV

19

17

18

31

29

44

72

76

 

 

 

Note that the = congenital anomalies data make it possible to

imagine the change = in shape of occurrence class vs. number of

diagnoses graphs = got by increasing the sample size, c.f. Gaston

(1994). The numbers demonstrate unambiguously the validity of

the rule in = epidemiology. Of course, with very small or large

total diagnosis = numbers the rule would appear distorted. As

mentioned above, = the origin of the rule is probably the (nearly)

lognormal = distribution of the diagnosis frequencies. Indeed we

found that the = truncated lognormal distribution fitted the

diagnosis = frequencies well. Computations were carried out using

the program package = DIVERSI 2.1 (Izs k 2003), containing

programs for = fitting and diversity calculations and available at

no cost by e- mail = from the author.

 

A general = conclusion is that analogous statistical conditions

lead to similar = statistical phenomena in remote scientific

fields. For = example, processes affecting plant species and

infectious diseases = (but not congenital diseases) show similar

traits from a = dynamical point of view. A remarkable link between

these processes can = be the data on the validity of Raunkiaer's

rule for = anthropochorous plants observed in isolated old houses

and small villages, = cited by Hanski(1982). At any rate, our

findings are = warning informations for researchers searching for

ecological = background of the rule. Naturally, possible

ecological = consequences of the rule and, in turn, the near-

lognormal = distribution, remains a question.

 

A note: not = mentioned in the article, we have observed signs of

latitudinal decline = of virus diversity moving north in England

(Hunter and = Izs=E1k 1993). This finding can be another data

arguing for a more = wide occurrence of a phenomenon often

mentioned in = ecology.

 

Acknowledgement

 

I should express my gratitude to Professor Mark Williamson for

his valuable = remarks and numerous corrections in the text.

 

References

 

Collins, S.L. & = S.M. Glenn, S.M. 1990. A hierarchical analysis

=A0=A0 of species' = abundance patterns in grassland vegetation.

=A0=A0 _Amer. Nat._ = 35: 633-648.

Dahl, E. _Rondane: = Mountain vegetation in south Norway and its

=A0=A0 relations to = the environment._ I Kommisjon hos H. Aschehoug &

=A0=A0 = Co. (W. Nygaard), Oslo. 374 p.

Gotelli, N.J. & = D. Simberloff. 1987. The distribution and

=A0=A0 abundance of = tallgrass prairie plants: a test of the core-

=A0=A0 satellite = hypothesis. _Amer. Nat._ 13:, 18-35.

Hanski, = I. 1982. Dynamics of regional distribution: the core and

=A0=A0 satellite = species hypothesis. _Oikos_ 38: 210-221.

Hunter, P.R. & = J. Izs=E1k. 1993. A latitudinal diversity gradient

=A0=A0 in virus = infections in humans in England and Wales.

=A0=A0 _Internat. = J. Epidem._ 22: 144-148.

Izs=E1k, J. 2003. DIVERSI 2.1: New version of a program package

=A0=A0 for = calculating diversity and related statistics. _Community

=A0=A0 Ecol._ 4: = 237-239.

Izs=E1k, J. & P. Juh=E1sz-Nagy. 1982. Studies of lognormality on

=A0=A0 mortality = statistics. _Biometr. J._ 24: 731-741.

McGeoch, M.A. & = K.J. Gaston. 2002. Occupancy frequency

=A0=A0 = distributions: patterns, artefacts and mechanisms. _Biol.

=A0=A0 Rev._ 77: = 311-331.

McIntosh, R.P. = 1962. Raunkiaer's law of frequency. _Ecology_ 43:

=A0=A0 = 533-535.

Papp, L. & J. = Izs=E1k. 1995. Bimodality in occurrence classes: a

=A0=A0 direct = consequence of lognormal distribution of abundances -

=A0=A0 a numerical experimentation. _Oikos_ 79: 191- 194.

Preston, F.W. 1948. The commonnes, and rarity, of species.

=A0=A0 _Ecology_ = 29: 254-283.

Raunkiaer, C. 1934. = The Life Forms of Plants and Statistical

=A0=A0 Plant = Geography. _Collected Papers of C. Raunkiaer._

=A0=A0 Clarendon = Press, Oxford.

 

 

BOOK REVIEW: LAND = SNAILS (AND SLUGS) OF BRITISH = COLUMBIA

From: Julia Sigwart [julia.sigwart@ucd.ie] originally published

=A0=A0 in the = American Malacological Society Newsletter vol. 36 (1)

=A0=A0 Spring 2005 = Page 4

 

Forsyth, Robert G. = 2004. _Land Snails of British Columbia._

=A0=A0 = Royal British Columbia = Museum Handbook, Royal British

=A0=A0 = Columbia Museum, Victoria, = BC, Canada. iv+188 p. =

=A0=A0 ISBN = 0-7726-5218-X [soft cover] Price: CDN$25.95 + postage.

=A0=A0 Available in = the USA from University of Washington Press, or

=A0=A0 e-mail shop@royalbcmuseum.ca

 

Local people in = British Columbia often refer to two varieties =

of slugs - = "good" slugs, the native giant Banana Slug _Ariolimax

columbianus_ and "bad" slugs, the invasive giant Black Slug

_Arion_ = spp.

 

In contrast, Land = Snails of British Columbia covers the natural

history of the = entire terrestrial gastropod fauna including 92

species of snails = and slugs. This book is the first

comprehensive = checklist and key to landsnails in western Canada,

and clearly, it = fills an important gap. I am personally

impressed that = Forsyth declines to cash in on the tremendous

popularity of the = Banana Slug (_Ariolimax columbianus_) and

gives it only equal = or less coverage than other species, many of

which are very = poorly studied. Every snail or slug has a one to

two-page = description including identification features,

distribution and = life history, and a selection of essential

primary references. = Forsyth uses contemporary classification

based on recent = work rather than relying on the classic Pilsbry

definitions, but = also includes common names for all taxa. The

most attractive = feature of the book is the identification key,

for use in the = field, presented in terminology that is precise

(and impartial) but = not intimidatingly technical. Copious black

and white = illustrations also help distinguish the animals. Since

no gastropods are = endemic to B.C., this publication will be of

great use to all malacologists west of the Rocky = Mountains.

 

The book is up to = the high standards of the other Handbooks

published by the = Royal BC Museum, and a great addition to any

natural history = library.

 

[For Robert = Forsyth's _Key to the slugs of British Columbia_

see BEN # 320, = Dec 30, 2003. - AC]

 

 

RE: A WHIFF OF = SCANDAL (BEN # CCCXLVI)

From: Toby = Spribille [tspribi@gwdg.de]

 

Hi = Adolf,

 

Your April Fool's = BEN story on the Peruvian orchid must be the

basis for a recent = evening _Krimi_" I watched when I was too

tired to sitting = and looking at lichens. It was in the German

evening _Krimi_ = series _Tatort_, set at a huge, posh orchid show

near = Lake Konstanz, with a guy who recently described an

illegally acquired = red lady's slipper murdered in cold blood by

a female orchid = fanatic who claimed it was her right to

describe. Like the = Selby story, this was portrayed as the

"orchid find = of the century", though in this case from Vietnam.

The customs = inspector who was caught on the crime scene trying

to steal the plant = later confessed to selling exotic orchids

illegally to an = Oriental collector - two crimes nailed with one

swipe. Remarkably, = the orchid involved looked not unlike that on

the = St. Petersburg Times website, = although it was much darker

red. The type = specimen, we were told, went to the herbarium at

the = University of Konstanz. I just found the episode online,

under the name _Der = Name der Orchidee_, at

htt= p://www.daserste.de/tatort/sendung.asp?datum=3D06.03.2005

 

All the = best,

Toby

 

[_Der Name der = Orchidee_ (SWR) Klara Blum (Eva Mattes) Sonntag,

6. M„rz 2005 = im Ersten "Alle jagen den roten Frauenschuh" Guess

the Chief = Botanist's name in this story! - His name was Dr.

Klaus Raven! - = AC]

 

________________________________________________________________

 

Subscriptions: http://victoria.tc.= ca/mailman/listinfo/ben-l

Send submissions to = aceska@telus.net

BEN is archived at = http://www.ou.edu/cas/bo= tany-micro/ben/

________________________________________________________________

------=_NextPart_000_0005_01C54426.28B90FB0-- From aceska@victoria.tc.ca Mon Apr 18 23:14:09 2005 From: aceska@victoria.tc.ca (Adolf Ceska) Date: Mon, 18 Apr 2005 15:14:09 -0700 Subject: [BEN-L]BEN # 347 - Post Scriptum Message-ID: <001501c54463$f58df720$0828b440@HPLAPTOP001> Apologies. Some people did not receive BEN # 347 correctly. I tried to send BEN # 347 with all the fancy graphics in Bryce Kendrick's article and the format I used was not compatible with many non-Microsoft systems. This attempt also made the BEN files far too long compared with the ordinary BEN issues. If you want to see BEN # 347 in the archives, please, visit http://www.ou.edu/cas/botany-micro/ben/ben347.html Both leading articles of the BEN # 347 deal with the so-called Raunkiaer's rule. Izsak Janos gives a short introduction to this rule in the first paragraph of his article. That paragraph and the literature cited there will give you better insight in this peculiar rule that used to be one of the shibboleths of the European phytosociology. Apologies again, I won't experiment with this mailing list any more. All the best, Adolf Ceska From aceska@victoria.tc.ca Wed Apr 27 00:23:32 2005 From: aceska@victoria.tc.ca (Adolf Ceska) Date: Tue, 26 Apr 2005 16:23:32 -0700 Subject: [BEN-L]BEN # 348 Message-ID: <000001c54ab6$f9dbc4c0$0828b440@HPLAPTOP001> BBBBB EEEEEE NN N ISSN 1188-603X BB B EE NNN N BBBBB EEEEE NN N N BOTANICAL BB B EE NN NN ELECTRONIC BBBBB EEEEEE NN N NEWS No. 348 April 26, 2005 aceska@telus.net Victoria, B.C. ----------------------------------------------------------- Dr. A. Ceska, P.O.Box 8546, Victoria, B.C. Canada V8W 3S2 ----------------------------------------------------------- IDENTIFICATION AND DISTRIBUTION OF THE SMALL WHITE WATER-LILIES, _NYMPHAEA TETRAGONA_ AND _N. LEIBERGII_, IN NORTHWEST TERRITORIES From: P. M. Catling, Biodiversity, National Program on Environmental Health, Agriculture and Agri-food Canada, Wm. Saunders Bldg., Central Experimental Farm, Ottawa, Ontario, Canada K1A 0C6 [catlingp@agr.gc.ca] Cody (1979) and Porsild and Cody (1980) reported _Nymphaea tetragona_ Georgi ssp. _leibergii_ (Morong) Porsild in Northwest Territories (NWT) on the basis of a specimen collected on an island in the Simpson group in Great Slave Lake, 40 miles NE of Resolution (E. A. Preble 243, US, see Porsild 1939). Recently Wiersema (1996, 1997) has recognized two taxa in North America: _Nymphaea leibergii_ Morong, which occurs mostly in eastern and central North America, and _Nymphaea tetragona_, which occurs in northwestern North America and Eurasia. _Nymphaea tetragona_ is distinguished by a prominent ridge at the insertion of the sepals which is lacking in _N. leibergii_ (Wiersema 1997a,b, Crowe and Hellquist 2000, Hellquist 2003). Previously all small white water- lilies in North America were referred to _N. tetragona_ ssp. _leibergii_. Wiersema reported _Nympaea tetragona_ from NWT on the basis of a specimen collected from a small lake 25 miles from Yellowknife on the road to Fort Rae (Murdy s. n., 1 Aug. 1961, KNK). As a result of the split _N. tetragona_ is actually a new record for NWT (not adequately explained in the recent compilation of additions - see Catling et al. 2005). Questions have arisen regarding the the identity other collections, specifically whether they are referable to _N. tetragona_ or to _N. leibergii_ (which occurs close to the NWT border in British Columbia) and is also present in northern Saskatchewan (Wiersema 1997). An examination of all the NWT collections readily available (see below) revealed that both _N. leibergii_ and _N. tetragona_ occur in NWT. Identification of specimens: The identity of the Preble collection (cited above) at the US National Museum has not been checked. The distribution map produced by Hultn and Fries (1986) shows four locations in NWT, one being the Resolution site (Preble), the two northernmost being near Yellowknife and the other being near to Fort Smith and possibly based on a specimen collected right on the Alberta- NWT border (17 July 1950, Cody & Loan 4500, DAO) cited by Wiersema (1996) under Alberta. These same four locations were shown by McJannet et al. in 1995. The basis for the locations shown near Yellowknife may be the published reports of Thieret (1963, 1964) evidently overlooked by Porsild and Cody (1980). In his 1963 catalogue of the flora of the Yellowknife highway, Thieret noted under _Nymphaea tetragona_ Georgi ssp. _leibergii_ (Morong) Porsild that it was: "seen only once, in a muck bottom lake, among Nuphar, mile 35.5 S [meaning 35.5 miles west of Yellowknife] 8328. In full flower on July 30." This specimen is presumably at F (Field Museum in Chicago) where most of the collections from Thieret's survey are deposited. In his 1964 description of vegetation along the Yellowknife highway Thieret states: "...Ray Murdy tells me that in 1963 he observed the species "here and there" in almost all of the medium to large lakes he studied along the highway from mile 10 S to mile 39 S." Thus of the 4 locations plotted, specimens are known from 3, and 2 of the specimens are referable to _N. tetragona_ based on examination by Wiersema. Four recent collections of small water-lilies are also attributable to _Nymphaea tetragona_ including: pond no. 2, W of Yellowknife at 62.4792 ̊N, -114.7280 ̊W, P. M. Catling & M. Fournier, 21 July 2003 (DAO); pond no. 124, W of Yellowknife at 62.5625 deg. N, -115.0868 deg. W, P. M. Catling & M. Fournier, 21 July 2003 (DAO); with _Chara_ in pond in Spruce woods, 15 km N of Fort Simpson at 61.9124 deg. N, -121.7005 deg. W, P. M. Catling 102 & B. Kostiuk, 24 July 2004 (DAO); shallow wetland, Deh Cho area, 61.6225 deg. N, -121.1002 deg. W, G. Allen 91, 10 Aug. 2004 (DAO). On the other hand, one recent collection is referable to _Nymphaea leibergii_: Camsell Ferry at 62.1567 deg. N, 122.4908 deg. W, L. Kershaw 15, 2003 (DAO). The recent report of _Nymphaea leibergii_ (sub _N. tetragona_ ssp. _leibergii_) from Alaska (Cook and Roland 2002) is presumably an error based on material of _N. tetragona_ since _N. leibergii_ does not occur in Alaska (Wiersema 1997) where _N. tetragona_ is widespread. Literature Cited Catling, P. M., W. J. Cody & G. Mitrow. 2005. A compilation of additions to the flora of the continental portions of Northwest Territories and Nunavut. Botanical Electronic News. In press. Cody, W. J. 1979. Vascular plants of restricted range in the continental Northwest Territories. Syllogeus 23. National Museum of Natural Sciences, Ottawa. Cody, W. J. & K. L. Reading. 2005. Additions and range extensions to the vascular plant flora of the continental Northwest Territories and Nunavut, Canada, III. _Canadian Field- Naturalist_. [In press] Cook, M. B. & C. A Roland. 2002. Notable vascular plants from Alaska in Wrangell-St. Elias National Park and Preserve with comments on the floristics. _Canadian Field-Naturalist_ 116(2): 192- 304. Crowe, G. E. & C. B. Hellquist. 2000. _Aquatic and Wetland Plants of Northeastern North America_. University of Wisconsin Press. 480 p. Hellquist, C. B. 2003. _Nymphaea leibergii_ Morong, Pygmy Water- lily, conservation and research plan for New England. 17 p. www.newfs.org/pdf/nymphaealeibergii.pdf Hultn, E. & M. Fries. 1986. _Atlas of North European vascular plants north of the Tropic of Cancer. I Introduction, Taxonomic Index to the Maps 1 - 996, Maps 1 - 996._ Koeltz Scientific Books. Knigstein, Germany. 498 p. McJannet, C. L., G. W. Argus & W. J. Cody. 1995. _Rare Vascular Plants in the Northwest Territories._ Syllogeus No.73. 104 p. Porsild, A. E. 1939. _Nymphaea tetragona_ Georgi in Canada. _Canadian Field-Naturalist_ 53(4): 48-50. Porsild, A. E. & W. J. Cody. 1980. _Vascular plants of continental Northwest Territories._ National Museums of Canada, Ottawa. 667p. Thieret, J. W. 1963. Botanical Survey along the Yellowknife highway, Northwest Territories, Canada I. Catalogue of the flora. _Sida_ 1(3): 117-170. Thieret, J. W. 1964. Botanical Survey along the Yellowknife highway Northwest Territories, Canada II. Vegetation. _Sida_ 1(4): 187-239. Wiersema, J. H. 1996. _Nymphaea tetragona_ and _Nymphaea leibergii_ (Nymphaeaceae): two species of diminutive water- lilies in North America. _Brittonia_ 48(4): 520-531. Wiersema, J. H. 1997. _Nymphaea_ Linnaeus. Pp. 71-77 in Flora of North America Editorial Committee, eds. _Flora of North America Volume 3, Magnoliophyta: Magnoliidae and Hamamelidae._ Oxford University Press, New York. http://www.efloras.org/florataxon.aspx?flora_id=1&taxon_id=200007090 RARE ANNUAL PLANTS - PROBLEMS WITH SURVEYS AND ASSESSMENTS From: Dana Bush [dbush@axys.net] and Jane Lancaster, Prairie Conservation and Endangered Species Conference, February 28, 2004; [final draft submitted February 8, 2004] Abstract Rare annual plants may have widely fluctuating populations, may or may not have abundant seed banks, are often adapted to disturbances, and may rely on metapopulations for their long term persistence. These characteristics influence the way we design rare plant surveys, assess the status and or threats, and design recovery plans or mitigation. Surveys and assessments should include historical locations, locations with few individuals, and all suitable habitat (even if empty) in close proximity to known populations. Information on seed bank size and viability, and dispersal distances, is needed to assess the status and potential threats to rare annual plants. Characteristics of rare annual species Rare plants typically have few occurrences and may have small populations. These small populations are more susceptible to stochastic events (Primack 2002), often have low pollination rates (Dieringer 1999; Wolf 2001), decreased seed viability or seed production (Fischer and Matthies 1998; Wolf 2001; Watson, Uno, McCarty and Kornkven 1994; Brys et al. 2004), and low genetic variation (Ellstrand and Elam, 1993; Primack 2002; Watson et al. 1994; Hackney and McGraw 2001). The importance of small isolated populations, on the long term persistence of a species, depends on how the species reproduces, whether it needs insects to assist in pollination, and the characteristics of the gene pool (Holderegger and Schneller 1994; Heschel and Paige 1995; Sipes and Tepedino 1995; Husband and Barrett 1996; Schemske, Husband, Ruckelshaus, Goodwillie, Parker and Bishop 1994). Generally, this information is unavailable for plant species at risk in Alberta, many of which are peripheral to core populations. Species specific information may be found in publications about populations in other jurisdictions, but there is no guarantee that the information will be applicable to peripheral populations as the genetics may be distinctly different (Lesica and Allendorf 1995), nor can one confidently extrapolate from more common species in the same genus (Kunin and Shmida 1997). Rare annual plants add a layer of complexity to the equation. Annual plants only grow for one year, and a large portion of the life cycle is seed. Plant numbers often fluctuate wildly from year to year depending on the seed production in previous years, germination of seedlings and environmental conditions (e.g. timing and amount of rainfall) (Fischer and Matthies 1998; Harrison, Maron and Huxel 1999; Primack 2002; Primack and Miao 1992). In addition, annual plants are often adapted to disturbances such as fire, land slides, grazing or flooding, and are often out competed in later successional stages (Hayes and Holl 2003; Watson et al. 1994; Harrison et al., 1999). For example, in Alberta we have found woollyheads (Psilocarphus elatior), smooth Boisduvalia (Boisduvalia glabella), and chaffweed (Anagallis mimina) only when spring or summer precipitation is sufficient to create ponding in ephemeral prairie wetlands. Additionally, the wetland area must be grazed sufficiently that taller perennial species are kept short and mineral soils are exposed. Seed bank Of the seed produced each year by annual plants, some portion is non-viable, some is lost to seed predators, some form seedlings, and some is stored in the seed bank. Seed bank and germination ecology are especially important to annual plants, but information on them is extremely difficult and time-consuming to gather (Elzinga, Salzer and Willoughby 1998; McCue and Holstford 1998). Most annuals have small seeds. Small seeds tend to remain viable longer than large seeds (Guo, Rundel and Goodall 1999) but the seed may or may not persist in the seed bank (Watson et al. 1994), and the seed may be abundant or rare, depending on the species (Guo, Rundel and Goodall 1999). The presence of abundant seed in the seed bank influences the genetics and hence the fitness of a population. Seeds germinating from the seed bank are "composed of progeny produced in many generations and represent migration from the past" (McCue and Holtsford 1998). The seed bank may have a broader genetic diversity than the current population of plants, and therefore may compensate for the harmful consequences of genetic drift or inbreeding, characteristic of small populations (McCue and Holtsford 1998; Ellstrand and Elam 1993). Fluctuating population Many annual plant populations vary widely in size from year to year depending on environmental conditions, such as moisture or disturbance. The degree of fluctuation is recognized as an important criteria in assessing the status of animal and plant species at risk (IUCN criteria B and C). For annual plants, fluctuation in plant numbers from year to year can be a substantial risk factor if there is no dormant seed bank, for the very small populations at the low point of the fluctuation have a high risk of losing valuable genes or losing entire populations. If, however, only a portion of the seed within the seed bank germinates in a given year then the fluctuating population may not be a serious risk factor. In some cases, what appears to be a local extinction may simply be prolonged seed dormancy (McCue and Holtsford 1998; Lesica and Steele 1994). This ability to persist as dormant seeds is an "escape in time" from environmental harshness (Harrison et al. 1999) that plants use, as opposed to an "escape in space" that mobile animals use. It is an effective survival mechanism, but makes the task of assessing the status of an annual species more difficult for botanists. Metapopulations Plant populations move. Very slowly. Plant populations that are found in isolated patches rely on the movement of pollen or seeds within metapopulations to maintain their genetic diversity. (A metapopulation is made up of a shifting mosaic of populations linked by some degree of migration (Primack 2002)). Even common plant species suffer reduced seed set and smaller populations when isolated (Lienert and Fischer 2003; Soons and Heil 2002), and species with small populations, short life cycles, or high habitat specificity are even more susceptible (Fischer and Stcklin 1997). Some species, however, seem to have adapted to small populations and limited gene flow (Holderegger and Schneller 1994). Metapopulations may be structured around one central core population that provides pollen or seed for numerous smaller populations. If the core population is eliminated, then the surrounding populations will also go extinct (Primack 2002). In addition, empty but suitable microsites might be necessary for long-term persistence of a metapopulation in a balance between local extinctions and recolonizations (Hanksi Moilanen and Gyllenberg 1996; Primack 2002). Long distance dispersal of seeds, however, is often rare and highly episodic, depending on a combination of unusual occurrences (Wolf 2001). Local populations, especially those in clusters, are more likely to produce seeds, and are more likely to recolonize a vacant habitat (Wolf 2001). Populations of annual plants farther than 100 m (Primack and Miao 1992) or 300 m (Harrison et al. 1999) from each other, have higher rates of extinction and fewer recolonization events than close populations. Primack and Miao (1992) conducted seeding studies and concluded that "Animals walking and digging through the soil, plus the action of wind and water flow, apparently do not move seeds any significant distance once they have landed on the soil surface". It appears that while pollination may occur over large areas, seed dispersal is restricted to small areas in most years. Meta-population theory is confounded by two additional factors when dealing with annual plants. Firstly, when species have persistent seed banks, or are capable of long term vegetative reproduction, the local extinction and recolonization rates are obscured, and it may be difficult to discern the dispersal rates in space versus time (Wolf 2001). Secondly if nearby populations fluctuate independently, then there is more potential for rescue and recolonization than if populations within dispersal range of one another behave synchronously (Harrison et al. 1999). Asynchronous populations take advantage of "escape in time" where populations produce seed in different years under different conditions. This means that a serious large scale event such as a large flood, fire, or hail storm would only eliminate the seed production from one population rather than the entire metapopulation. Survey techniques Survey techniques must be adapted to the characteristics of rare annual plants. Because a large portion of life cycle is as seed, the number of individuals visible above ground may fluctuate widely and are not easy to identify. Surveys should always include a thorough search of historical records and a survey of the historical locations. The timing of the surveys should be flexible to reflect the moisture conditions and the disturbance regimes required by the species in question. Potential habitat should be examined in several years, under different climatic conditions, since "the absence of individuals above ground in any given year does not necessarily mean that the population is truly extinct" (Harrison et al. 1999). All potential habitat in close proximity to the survey area should be surveyed, for it is often the existence of at least a portion of the metapopulation that will ensure the long-term survival of the species or subpopulation. Because annual plants are often associated with disturbances, surveys should carefully inspect these areas, even though we intuitively associate rare plants with undisturbed habitats. In Southern Alberta, we have found American pellitory (Parietaria pensylvanica) under shrubs where cattle gather for shade and churn the soil. We have also found smooth boisduvalia and chaffweed under irrigation pivots in cultivated fields, and sand verbena is found in open, shifting sand dunes. Assessment The assessment of threats or status of rare annual plants is difficult. Most research on conservation biology has been done for animals, and there has been little work done on the role of metapopulations and seed banks for rare annual plants (Ellstrand and Elam 1993; McCue and Holtsford 1998). Little work has been done on plants that are rare in Alberta, so we don't know if a species has a persistent seed bank, how long the seeds lie dormant, or how far the seeds are dispersed, much less the reasons for rarity. Based on the previous discussion several points should be considered when assessing the threat or status of a rare annual plant species: 1. the absence of plants at a historical location does not imply extinction: a seedbank may be present; 2. the presence of one individual may indicate that there is a viable seedbank; 3. the presence of many individuals, however, does not mean that there is a viable seedbank; 4. habitat that looks suitable but has no rare plants this year, may have a population in a different year (due to migration or seed-bank germination); 5. adjacent populations may be critical to the survival of a population (and vice versa); 6. past disturbances do not preclude rare plants; 7. future disturbances, such as a pipeline, fire or grazing, may increase the population (or may decrease it); 8. long-term changes in disturbance regimes or climatic conditions may affect the viability of populations. The Alberta Endangered Species Conservation Committee and The Committee on the Status of Wildlife in Canada use the criteria established by the International Union for the Conservation of Nature (IUCN 2001) to assess the status of plants and animals at risk. One of the criteria (B - extent of occurrence) considers extreme fluctuations in the extent of occurrence, area of occupancy, number of locations or subpopulations, or number of mature individuals. The number of mature individuals is defined as " the number of individuals known, estimated or inferred to be capable of reproduction. When estimating this quantity the following points should be borne in mind: Where the population is characterised by natural fluctuations the minimum number should be used . ... For plants with seed banks use the juvenile period + either the half-life of seeds in the seed bank or the median time to germination. Seed bank half-lives commonly range between <1 and 10 years." Primack (2002) suggests that for annual plants the effective population size should be somewhere between the lowest and the highest number of breeding individuals, and proposed using the Harmonic Mean of several years data. Ne = t/(1/N1 + 1/N2 + ... + 1/Nt). McCue and Holtsford (1998) point out that the impact of even a small number of seeds in the seed bank can have a significant impact on the effective population, and suggest that the Ne should include an estimate of viable seeds/population area. This, however, assumes that you know the size of the seed bank and how long the seeds persist. Without data on the seed bank, we run the risk of under- estimating the effective population (by ignoring a viable seed bank) or under-estimating the impacts of population loss (by assuming that a fluctuating population will have a seed bank, and is therefore safe). Recovery Plans and Mitigation Mitigation of impacts to rare plants should always concentrate on protecting existing populations rather than using experimental techniques to establish new populations (Bush 2001). Successful introductions likely depend "on the fortuitous combination of a particular genotype in a suitable microsite in a particular year" (Primack and Miao 1992). If experimental introductions are attempted, they should involve seeding numerous potential microsites in several years (Primack and Miao 1992). In summary, mitigation of human impacts to rare annual plant populations should: 1. protect historical populations - even if plants are absent; 2. conserve habitat that has a high potential - even if plants are absent; 3. confine impacts to dormant periods, prior to germination or after seed set; 4. conserve the seed bank; 5. maintain the natural disturbance regime; 6. maintain the environmental conditions (the shape of the wetland, slope, etc); 7. collect and re-distribute seed to numerous potential sites in several years; 8. monitor the results. Monitoring Monitoring is essential to any mitigation project that involves disturbing rare communities and rare plant species. Monitoring is the only way to assess if the mitigation was successful or not, and to make informed choices about future mitigation strategies. Successful mitigation techniques can therefore be used with greater confidence and unsuccessful ones reevaluated or avoided. Many of the techniques recommended for rare plant mitigation are experimental, and little is known about the biology and reproductive capacity of individual species (Allen 1994; Primack 2002; Falk, Millar and Olwell 1996). To account for the natural fluctuations in populations, monitoring should be done regularly and for several years. Remember, that absence might be the result of prolonged dormancy not extinction. When monitoring for recovery plans, data should be collected from years when the plants are absent as well as from years when they are present, to fully describe their response to environmental fluctuations. When monitoring to determine if mitigation was successful (assuming the budget is very limited), it may be appropriate to survey in selected years (3 years in 5, or 5 in 12) to take advantage of years with good growing conditions (provided you understand what conditions are needed for germination). In either case, the results should be published so that we can increase our understanding or rare plant biology and mitigation. Conclusions Rare annual plants have a suite of unique characteristics that affect our ability to assess their status and to develop recovery and mitigation plans. Rare annual plant species may naturally experience large fluctuations in plant numbers, and may have dormant seed banks which are difficult to assess in terms of size and viability. In addition, they may rely heavily on the presence of nearby populations and disturbance for their long-term persistence. These characteristics must be included into the design of field surveys, into the thought processes behind assessing the status and the threats to the population, and when designing mitigation and monitoring programmes. References Allen, W. H. 1994. Reintroduction of Endangered Plants. _BioScience_ 44(2): 65-68. Brys, Rein, Hans Jacquemyn, Patrick Endels, Fabienne Van Rossum, Martin Hermy, Ludwig Triest, Luc De Bruyn & Geert D. E. Blust. 2004. Reduced reproductive success in small populations of the self-incompatible _Primula vulgaris_. _Journal of Ecology_ 92: 5-14. Bush, C. Dana. 2001. Rare Plant Mitigation for Linear Disturbances. In: _Proceedings of the 25th Annual Canadian Land Reclamation Association and the 4th Annual International Affiliation of Land Reclamationists Meetings. September 17- 20, 2000._ Edmonton, Alberta. Dieringer, Gregg. 1999. Reproductive biology of _Agalinis skinneriana_ (Scrophulariaceae), threatened species. _Journal of the Torrey Botanical Society_ 126(4): 289-295. Ellstrand, Norman C. & Diane R. Elam. 1993 Population genetic consequences of small population size: Implications for plant conservation. _Annual Rev. Ecol. Syst._ 24: 217-242. Elzinga, Caryl L., Daniel W. Salzer & John E. Willoughby. 1998. _Measuring & Monitoring Plant Populations._ BLM Technical Reference 1730-1. 477 pp. Falk, Donald A., Constance I. Millar, & Margaret Olwell. (editors). 1996. _Restoring Diversity. Strategies for Reintroduction of Endangered Plants._ Island Press, Washington D.C. Fischer, Markus and Diethart Matthies. 1998. Effects of population size on performance in the rare plant _Gentianella germanica_. _Journal of Ecology_ 86: 195-204. Fischer, Markus and Jrg Stcklin. 1997. Local extinctions of plants in remnants of extensively used calcareous grasslands 1950-1985. _Conservation Biology_ 11(3): 727-737. Guo, Qinfeng, Philip W. Rundel & David W. Goodall, 1999. Structure of desert seed banks: comparisons across four North American desert sites. _Journal of Arid Environments_ 42: 1- 14. http://www.idealibrary.con Hackney, Erin E. and James B. McGraw. 2001. Experimental Demonstration of an Allee Effect in American Ginseng. _Conservation Biology_ 15(1): 129-136. Hanski, Ilkka, Atte Moilanen, and Mats Gyllenberg. 1996. Minimum viable metapopulation size. _The American Naturalist_ 147(4): 527-541. Harrison, Susan, John Maron, and Gary Huxel. 1999. Regional turnover and fluctuation in populations of five plants confined to serpentine seeps. _Conservation Biology_ 14(3): 769- 779. Hayes, Grey E. and Karen D. Holl. 2003. Cattle grazing impacts on annual forbs and vegetation composition of mesic grasslands in California. _Conservation Biology_ 17(6): 1694- 1702. Heschel, M.S. and K.N. Paige, 1995. Inbreeding Depression, Environmental Stress, and Population Size Variation in Scarlet Gilia (Ipomopsis aggregata). _Conservation Biology_ 9: 126-133. Holderegger, R. and J.J. Schneller, F.L.S. 1994. Are small isolated populations of _Asplenium septentrionale_ variable? _Biological Journal of the Linnean Society_, 51: 377-385. Husband, Brian C. and Spencer C.H. Barrett. 1996. A metapopulation perspective in plant population biology. _Journal of Ecology_ 84: 461-469. Kunin, W.E. and A. Shmida, 1997. Plant Reproductive Traits as a Function of Local, Regional, and Global Abundance. _Conservation Biology_ 11: 183-192. Lesica, Peter, and Brian M. Steele, 1994. Prolonged Dormancy in Vascular Plants and Implications for Monitoring Studies. _Natural Areas Journal_ 14: 209-212. Lesica, Peter and Fred W. Allendorf. 1995. When are peripheral populations valuable for conservation? Conservation Biology 9(4): 753-760. Lienert, Judit, and Markus Fischer. 2003. Habitat fragmentation affects the common wetland specialist _Primula farinosa_ in north-east Switzerland. _Journal of Ecology_ 91: 587-599. McCue, Kimberlie A. and Timothy P. Holtsford. 1998. Seed bank influences on genetic diversity in the rare annual _Clarkia springvillensis_ (Onagraceae). _American Journal of Botany_ 85(1): 30-36. Primack, Richard B. 2002. _Essentials of Conservation Biology_. Sinauer Associates, Sunderland, MA. Primack, Richard B. and S.L. Miao. 1992. Dispersal and limit local plant distribution. _Conservation Biology_ 6(4): 513- 519. Schemske, Doduglas W., Brian C. Husband, Mary H. Ruckelshaus, Carol Goodwillie, Ingrid M. Parker, and John G. Bishop. 1994. Evaluating approaches to the conservation of rare and endangered plants. _Ecology_ 75(3): 584-606 Sipes, S.D. and V.J. Tepedino, 1995. Reproductive Biology of the Rare Orchid, _Spiranthes diluvialis_: Breeding System, Pollination, and Implications for Conservation. _Conservation Biology_ 9: 929-938. Soons, Merel B. and Gerrit W. Heil. 2002. Reduced colonization capacity in fragmented populations of wind-dispersed grassland forbs. _Journal of Ecology_ 90: 1033-1043. The International Union for the Conservation of Nature. 2001. _IUCN Red List Categories: Version 3.1._ Prepared by the IUCN. Watson, Linda E., Gordon E. Uno, Newell A. McCarty, and Amy B. Kornkven. 1994. Conservation biology of a rare plant species, _Eriocaulon kornickianum_ (Eriocaulaceae). _American Journal of Botany_ 81(8): 980-986. Wolf, Amy. 2001. Conservation of endemic plants in serpentine landscapes. _Biological Conservation_ 100: 35-44. COAST MOUNTAIN FIELD INSTITUTE LAUNCHES SEASON 2 WITH 18 FIELD COURSES IN SOUTHWESTERN BC. From: Rebecca Porte [rporte@cmfi.ca] & Terry McIntosh [ginkgo@shaw.ca] Coast Mountain Field Institute (CMFI) is beginning it's second year of programming in a few weeks. Last year CMFI was established as a non-profit organization designed to provide field- based educational opportunities on a wide range of topics, from botany to natural and cultural history, nature- related arts, family-oriented natural history programs, to stewardship and conservation. Courses are meant for a wide variety of audiences, and feature small group sizes, interesting topics, and beautiful locations. Instructors include some of BC's most renowned biologists and naturalists. The main goals for CMFI are to help enhance people's knowledge and understanding, while inspiring a continuing appreciation, for the province's wild landscapes, and to develop a desire to foster stewardship for future generations. We have designed eighteen courses for 2005. Botany related courses include a 2 day program on Salt Spring Island examining Garry Oak Ecosystems with Terry McIntosh (May 14 -15). Other botany courses include a wildflower investigation at Manning Park, Plants for Hikers on Keats Island, and the a fungi workshop on the Sunshine Coast (not quite botany, but close enough for us). Examples of other courses offered for 2005 include Okanagan Songbird Migration led by Dick Cannings, BC Rivers: From Urban To Wild led by Mark Angelo, Danny Catt, and Bob Gunn, and Ethnoecology of the Straits Landscape, led by Dr. Brenda Beckwith, Cheryl Bryce, and Marilyn Lambert. The programs promise to be interesting, informative, and relevant. For a complete listing of our courses and for more information about our institute, please visit our website at http://www.cmfi.ca . NEW BOOK: MOUNT ST. HELENS - ECOLOGICAL RESPONSES Dale, Virginia H., Swanson, Frederick J., & Crisafulli, Charles M. (Eds.) May 2005. Ecological Responses to the 1980 Eruptions of Mount St. Helens. Springer Verlag, New York, NY. Approx. 745 p., ISBN 0-387-23868-9 [hard cover], Price: US$79.95 ISBN 0-387-23850-6 [soft cover], Price: US$39.95 Not yet published The eruption of Mount St. Helens on May 18, 1980, had a momentous impact on the fungal, plant, animal, and human life from the mountain to the far reaches of the explosion's ash cloud and mudflows. Although this intense natural event caused loss of substantial life and property, it also created a unique opportunity to examine a huge disturbance of natural systems and their subsequent responses. Based on one of the most studied areas of volcanic activity, this book synthesizes the ecological research that has been conducted for twenty- five years since the eruption. Research from geology as well as plant and animal ecology has been integrated in this unprecedented look at the complex interactions of biological and physical systems in the response of the volcanic landscape. Lessons from the volcano inform our larger understanding of ecosystem disturbances, natural processes, and the impact of land-use practices. Included are results of significant and long-term research on vegetation, mycorrhizae, plant and animal interactions, arthropods, amphibians, mammals, fish, lakes, nutrient cycling, geomorphology, and environmental management. This comprehensive account will be of value to those interested in natural history, ecology, disturbance, conservation biology, limnology, geoscience, and land management. Questions about what actually happens when a volcano erupts, what the immediate and long-term dangers are, and how life reasserts itself in the environment are discussed in full detail. BEN NOW AVAILABLE BY RSS From: Scott D. Russell [srussell@ou.edu] In the great BEN tradition, as explained in Adolf Ceska's "Short History of BEN" (No. CCXLVII April 1, 2000 http://www.ou.edu/cas/botany-micro/ben/ben247.html), I learned about RSS ("Really Simple Syndication") as a way of providing news feeds and am incorporating it in a number of my web sites. The technology is growing rapidly in popularity this year. Major journals, newspapers, blogs and other websites have incorporated RSS as a means of communication, written in a simplified version of XML (the extensible form of HTML -- the language of the web). RSS feeds from many sites can be consolidated into a collection of news that is read by a special reader, an RSS reader. Anyway, BEN now has an RSS feed! The feed is linked at the BEN web site by an orange tag that says "XML" (the traditional RSS indicator). If you import this into an RSS reader, then you will have BEN articles as news items. With some RSS readers, you can click the orange icon, drag and drop it, or copy the link into an import utility. Is this of any practical use? -- you be the judge. Daniel Mosquin of the University of British Columbia Botanical Garden and Centre for Plant Research has crafted the BEN newsfeed into his site on the following web page: http://www.ubcbotanicalgarden.org/resources/botanicalelectro nicnews.php His site uses the newsfeed in building part of the website and is updated whenever the newsfeed is changed, providing breaking BEN news, for instance. If you decide to see what an RSS newsreader is, I would suggest a free one (e.g., Lektora at http://www.lektora.com/ is a good one, which becomes an integral part of Firefox or Internet Explorer web browsers and comes with about 30 pre-configured feeds) before you buy one. For more, here is my introduction to RSS in my Scott's Botanical Links site: http://www.ou.edu/cas/botanymicro/bot- linx/mar05.shtml#Mar29 ________________________________________________________________ Subscriptions: http://victoria.tc.ca/mailman/listinfo/ben-l Send submissions to aceska@telus.net BEN is archived at http://www.ou.edu/cas/botany-micro/ben/ ________________________________________________________________