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Redhead Fungal Biogeography.pdf - Mushroom Hobby

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Can. J. Bot. Downloaded from www.nrcresearchpress.com by Adolf Ceska on 10/11/11<br />

For personal use only.<br />

3004 CAN. J. BOT. \<br />

in 1983 (<strong>Redhead</strong> 1984b), i.e., coast to coast in 5 years. This<br />

pattern of distribution certainly brings to mind the anonymous<br />

quote cited in Smith and Weber (1980, p. 6), "<strong>Mushroom</strong>s are<br />

where you find them." The apparent hopelessness of studying<br />

the biogeography of mushrooms, as well as economical practices,<br />

have been contributing factors leading to the common<br />

practice of citing mushroom specimens in North American<br />

monographs by the state or province followed only by<br />

collector's numbers and no maps. For example, Lactarius<br />

glyciosmus (Fr.) Fr. was reported from unspecified locations<br />

in both Quebec and Ontario in addition to various other provinces<br />

and states by Hesler and Smith (1979). Ontario covers<br />

1 068 630 km2 and Quebec covers 1 540 681 km2, both span<br />

nearly 15" of latitude, and both have vegetation ranging from<br />

tundra to Carolinian hardwood forests.<br />

In questions of plant quarantine, legal issues concerning trafficking<br />

of illicit species, locating or protecting harvestable species,<br />

and in the formulation of national policies, it is<br />

imperative that some sense be made of the distributional patterns<br />

of macrofungi. Are there species truly endemic to Canada<br />

and not just known from a type locality in Canada? If a species<br />

is found in coniferous forests in British Columbia, and then in<br />

New York state, can we assume it occurs across the continent?<br />

If a fungus, new to North America, is found in Canada, where<br />

else in the world might it have been described? What were the<br />

mycofloristic elements that combined to form our present<br />

fungus flora?<br />

Comparable plant and lichen floras<br />

During the Pleistocene nearly all of Canada (Prest 1984),<br />

except for parts of the northern Yukon and the Arctic Archipel-<br />

ago (HultCn 1937), isolated parts of coastal British Columbia<br />

(Calder and Taylor 1968), and perhaps Newfoundland (Ahti<br />

1983; Brassard 1983, 1984; Steele 1983), was covered by con-<br />

tinental glaciers. In the past 8000 - 12 000 years, virtually all<br />

of Canada has been recolonized from elsewhere. HultCn (1937)<br />

suggested that some of the northern vascular plant flora of<br />

North America and Eurasia survived in isolated refugia, such<br />

as those mentioned above, from which they are radially<br />

spreading at different rates. Whitehead (1972) noted that much<br />

of the northern flora was displaced to the south, to form plant<br />

communities that differed from any extant flora. Some plant<br />

species have successfully recolonized circumpolar areas and<br />

others now have fragmented, disjunct distributions. Commonly<br />

recognized disjunctions among vascular plants are the eastern<br />

Asia - eastern North American disjuncts (Gray 1859; Wood<br />

1972), eastern North America - western North America dis-<br />

juncts (Schofield 1969; Wood 1972), amphi-Atlantic disjuncts<br />

(HultCn 1958), and amphitropical North America - South<br />

America disjuncts (Wood 1972). Culberson (1972), Schofield<br />

and Crum (1972), and Schofield (1972) have shown that<br />

lichens and bryophytes have nearly identical patterns of dis-<br />

junctions and contiguous ranges to those exhibited by vascular<br />

plants. Culberson (1972, p. 165) stated, "So similar in fact<br />

are the well documented ranges of lichens to the ranges<br />

of vascular plants that the conclusion that both result from<br />

the same physioecological and historical factors is inescap-<br />

able." With regard to the Canadian vascular plant flora,<br />

Porsild (1958) recognized eight major categories of plant<br />

distribution with additional subcategories: (i) Circumpolar<br />

(High-arctic Element, Arctic-alpine Element, Low-arctic Ele-<br />

ment); (ii) Amphi-Atlantic (Arctic Element, Subarctic Ele-<br />

ment); (iii) Amphi-Beringian, (iv) North American (Arctic<br />

Element, Boreal forest Element, Cordilleran Element, Pacific<br />

coast Element, Prairie and foothill Element, Southern hard-<br />

wood forest Element, Northern hardwood forest Element,<br />

Atlantic coastal plain Element); (v) Arctic Archipelago<br />

Endemic; (vi) Eastern Arctic Endemic Element; (vii) Western<br />

Arctic Endemic Element; (viii) Disjuncts. The disjunct distri-<br />

butions in North America can be further divided as done by<br />

Schofield and Crum (1972) for bryophytes. They recognized<br />

eastern American - East Asia disjuncts, tropical and sub-<br />

tropical - Southern Appalachian disjuncts, bipolar disjuncts,<br />

European - western North America disjuncts, as well as<br />

amphi-Pacific, amphi-Atlantic, and arctic-alpine disjuncts.<br />

Brodo and Hawksworth (1977) categorized the distributional<br />

patterns of various epiphytic North American lichen genera<br />

slightly differently. They treated many of the disjuncts as spe-<br />

cies with fragmented circumboreal ranges, and therefore,<br />

included them with species with more complete circumboreal<br />

distributional patterns. Thus, their categories were (i) Circum-<br />

boreal -Circumpolar species (1. arctic-alpine element; 2. low-<br />

arctic element; 3. amphi-Atlantic, southern element; 4. boreal<br />

forest element; 5. Appalachian - Great Lakes, temperate; 6.<br />

oceanic-suboceanic species; 7. western American - Euro-<br />

pean disjuncts); (ii) Asian affinities (8. bicoastal, Appala-<br />

chian - west coast disjuncts); (iii) North American endemics<br />

(9. North Pacific; 10. coastal lowland; 11. lowland to western<br />

montane humid forests; 12. Western montane and inter-<br />

montane dry forests; 13. Appalachians; 14. northeastern<br />

coastal plain; 15. Central American highlands).<br />

Current status of macromycete mycogeography<br />

Relatively few studies have been made of the distributions of<br />

macromycetes. Accumulation of accurate data is the most<br />

common problem. With fleshy fungi, detailed field notes are<br />

often required for precise determinations. Hence, relatively<br />

few herbarium specimens can be confirmed or redetermined<br />

accurately. The need for detailed notes slows the collecting<br />

process so that fewer collections are made. Added to these<br />

problems is the ephemeral nature of the fruitbodies. Another<br />

consideration of more importance in Eurasia than in North<br />

America, is the limitation of access by political boundaries.<br />

The latter factor severely limited the usefulness of maps of 50<br />

macromycetes prepared by the Committee for Mapping of<br />

Macromycetes in Europe (Lange 1974) and the two earlier<br />

maps by the committee- a an sen and Lange 1966). Contribu-<br />

tions were lacking from Spain, Portugal, Italy, and the USSR,<br />

and relatively few were received from Bulgaria and Ireland. To<br />

a lesser extent this occurs in North America. Kers (1988)<br />

mapped the disjunct European - western North American dis-<br />

tribution for the hypogeous ascomycete Geopora cooperi<br />

Hark. The species appears to abruptly stop at the border<br />

between Washington, U.S.A. and British Columbia, Canada,<br />

and again reappears in Alaska. This is clearly an artifact result-<br />

ing from monographers collecting only within their own<br />

country. Canadians have not collected many hypogeous fungi.<br />

To overcome some of the difficulties mentioned above, the<br />

European Mycological Congress chose 100 easily recognized,<br />

clearly defined macrofungi, e.g., Auriscalpium vulgare S. F.<br />

Gray, Strobilomyces floccopus (Vahl. : Fr.) Sacc., and<br />

Phaeolepiota aurea (Bull. : Fr .) Marie for mapping (Lange

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