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Organicism:
A Post Script on Units of Vegetation
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| Historical Perspective | |||||||||||||||||||||||||||||||||||
| It was discussed above that Nichols (1923) employed the continuum or individualistic concept of Gleason (1917) when developing a system of vegetation classification.Yet Nichols, like all others of the Anglo-American Tradition of plant ecologists except Gleason (Shimwell, 1971, p. 54), subscribed to a philosophical perspective of vegetation subsequently labeled organicism or the closely related holism. As an analogy or metaphor organicism was expressed in “purest” form by Clements, Phillips, and as quoted above, Smuts. An example of the application of organicism to vegetation came from Nichols (1923, p. 14): | |||||||||||||||||||||||||||||||||||
| “The Association
an Organic Entity. Characterized as above, a plant association may be
regarded in its entirety as an organic entity, and as such it occupies
a position in the field of ecological plant sociology which is homologous
in a general way to that occupied by an individual plant or specimen in
such fields of botany as plant morphology or plant taxonomy. As integral
parts of the larger community, plant societies bear a relation to the
association which is somewhat analogous to that borne by the various organs
of an individual plant to the plant as a whole” (Nichols, 1923, p.14).
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| The difference between the Clementsian and the Gleasonian interpretations of vegetation was the difference between organicism and individualism, two “completely antithetical” views (Barbour et al., 1999, p. 23) of whether plant communities are actual, real, naturally occurring units of vegetation (Clements) or artificial, arbitrary, human-contrived abstractions for purposes of description, classification, management, etc. of vegetation (Gleason). These diametrical perspectives came to be distinguished as Clements’ organismic and Gleasons’s individualistic or continuum theories (or hypotheses). These opposing views were basis of what was probably the most divisive, often bitter, debate within the Anglo-American or English Tradition of vegetation classification. Explanations of the organismic and individualistic schools of thought can be found in McIntosh (1985) and standard Plant Ecology texts (eg. Barbour et al., 1999, ps. 22-23, 182-183, 268, 294, 295, 302). | |||||||||||||||||||||||||||||||||||
| As of this discussion herein, the best comparison of the Clementsian and the Gleasonian philosophies--and they were philosophies, complete with metaphysical underpinnings--of vegetation was that of Eliot (2007). Review and reinterpretation of Clements' scientific description of plant succession in the analysis of Eliot (2007) showed a much greater depth of perception than that of almost all other readings of Clements', by both critics and disciples. In his interpretative analysis of the Clementsian model of plant succession Eliot (2007) concluded that contrary to a commonly held myth or misconception Clements did not propose a law of vegetation, but instead developed a framework from which to explain veggetational dynamics without laws. Furthermore, Clements and Gleason essentially agreed on the causes of this dynamics (Eliot, 2007). From this perspective it was interpretors of Clements such as Tobey (1981) and McIntosh (1985) who were niaeve and incorrect in their understanding of what Frederic Clements really meant and actually said. | |||||||||||||||||||||||||||||||||||
| Analytical comparison of the Clementsian and Gleasonian philosophies of vegetation by Eliot (2007) was clearly not the first and, most likely, will not be the last treatment of this purported hallmark dichotomy. To date, however, it was the most in-depth and, arguably, the most perceptive evaluation of the two "bookends" of Vegetation Science. | |||||||||||||||||||||||||||||||||||
| Study of these
two perspectives of vegetation (and especially the battle between them)
is interesting and instructive but beyond the context of the specific
vegetation units considered here because the Clementsian organismic interpretation
is the one that is the basis of biomes and range cover or dominance types.
The thrust of Gleason’s hypothesis— that plant communities are all individual
entities that are distributed along continua or gradients of innumerable
highly variable environmental factors— largely argues against predicatable,
recurrent units of vegetation. If, as Gleason argued (with credible scientific
evidence to confront that of Clementsian ecologists), units of vegetation
are just imaginitive abstractions and communities are merely individual
groups of plant species then classification units like associations would
be of little utility (perhaps especially so for purposes of standard management
practices). If species compositions of groups of plants are simply the
result of chance migrations of plant propagules over fluctuating habitats
then vegetation units such as associations are not distinct or definite
(ie. contrary to assertions by ecologists like Warming an association
cannot be regarded as a species or the formation as a genus; groups of
plants do not recur as if they were specific taxa). |
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| Carried to it’s
logical ends the individualistic argument could be seen as calling into
question the entire practice of classifying (but not mapping) vegetation.
If groups of plants are just individual, happenstance assemblages then
alternatively 1) there is either no such thing as, say, a dominance or
cover type or 2) there are countless cover types with each being an individual
abstraction that may never appear again. Either way, a range type would
be more or less meaningless. |
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| It was remarked previously that the “correctness” of one theory versus another or which school of thought was “closest” to ecological reality is irrelevant. Clements, Gleason, Tansley all made remarkable lasting contributions and ultimately all were recognized as eminent ecologists. | |||||||||||||||||||||||||||||||||||
| “The present American concept
of the community is a synthesis of Clement’s association unit hypothesis
with Gleason’s continuum-individualistic hypothesis, together with a recognition
that there may be several different kinds of associations, each explainable
according to a different model. We have come to understand that the classical
theories are inadequate for completely explaining and predicting vegetation
patterns, and we have come to appreciate that the scale of complexity
in nature makes the existence of a single model highly unlikely”. |
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|
-- Barbour et al. (1999, p. 185-186) |
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| Given that 1) the vegetation units relevant to range types are Clementsian in origin, 2) the Clementsian model is the cornerstone of Ecology as applied in professions like Range Management, Forestry, and Wildlife Management, and 3) the ecosystem concept grew out (or because) of organicism, which has been the most controversial (and likely the most misunderstood) aspect of the Clementsian paradigm, some consideration of organicism appeared worthwhile. | |||||||||||||||||||||||||||||||||||
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| From Vegetation to Ecosystem | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Top of page | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Obviously, Tansley
was an organicist. The holistic perspective was central to his revolutionary
ecosystem— the “quasi-organism”— concept . That “the whole is greater
than the sum of the parts” is the cornerstone of the ecosystem paradigm
which in turn is the centerpiece of faith in contemporary environmental
sciences. Yet, the organicism of Tansley and that of his dear friend were
two different interpretations and philosophical perspectives of a metaphor
long used in human sociological and political theory. |
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| The two major
things that made the difference between the Clements and Tansley perspectives—
the two distinctive ideas or, actually, philosophies— of the Anglo-American
Tradition of vegetation were: 1) Clements extreme organicism (the “social
or complex organism”) that was sometimes described almost metaphysically,
and 2) Clements limitation of his ecological unit— the biome or formation
(again, “superorganism”) and its subdivisions (eg. associations, faciations)—
strictly to organisms, the biotic components, whereas Tansley incorporated
into his ecological unit— the ecosystem (the “quasi-organism”)— both biotic
and abiotic components. |
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| From Clements’
perspective, habitat was included in his classification of vegetation
but only indirectly as habitat (= the abiotic environment) contributed
to the expressed vegetation, to the finished product (the climax and its
subdivisions or the distinct seral units). From Tansley’s perspective,
habitat factors had to become incorporated in studies of communities to
a greater extent than they had been if more knowledge was to be gained
about how nature, especially communities, operated. Clements opted to
continue to study vegetation and its development (plant succession) and
to perfect his description and classification of these; Tansley elected
to expand study beyond vegetation to everything imaginable within an area
of the landscape (ie. the ecosystem). |
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| The fact is that Clements and Tansley had two distinctly separate goals or objectives. Clements was describing and classifying vegetation (and, by extension, the biome). Clements’ classification and descriptions were based: 1) directly on physiognomy and dominance, 2) indirectly on habitat as expressed in the vegetation, and 3) interpretatively on vegetation development, his key feature, from keen observtion and experience. Tansley was establishing a brand new way of viewing holistic ecology, of studying the whole ecological world (the ecological system). Tansley’s new conceptual view changed Plant Ecology (Ecology in general) from descriptive evaluation of biotic communities to quantitative analysis of the entire ecological system (biota plus everything affecting them). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| This shift in
emphasis or redirection of scientific inquiry within a given discipline
was what Tobey (1981, p.
6-8, 110-119, 120-154 passim, 199, 203, 206-207, 213, 215) described as
a “paradigm shift” in the classical theory of scientific revoultions as
developed by Kuhn (1970, the second edition) in his highly provocative
The Structure of Scientific Revolutions. Within the existing scientific
field of Ecololgy Tansley proposed a theory which laid the groundwork
for what became an entirely new subdiscipline (Ecosystsem Ecology), a
new dominant area of active research. At the same time, pre-existing areas
of investigation like vegetation classification and plant succession either
remained at the same level of research activity or lost new scientists
to the emerging area of ecosystem studies. |
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| In his recent writings Kuhn was more specific as to meanings of "paradigm" and "paradigm shifts" and therefore the defining characteristics of scientific revolutions. Some of the most important of Kuhn's later works were bound as a single volume (Kuhn, 2000) that served as appendices or further interpretations of his view of scientific revolutions. In writings since publication of the second (1970) edition of Structure Kuhn stopped using the word paradigm as much as he could because he had "...totally lost control of it" (Kuhn, 2000, p. 211). "Paradigm was a perfectly good word until I messed it up" (Kuhn, 2000, p. 298). Given this situation with the physicist-turned historian of sicence who gave the scientific community the concept and term of "paradigm shift" it is perhaps advisable to de-emphasize this aspect of scientific revolutions and focus on features that remained central to Kuhnian theory. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|
The key or defining feature of scientific revolutions in Kuhnian theory remained "incommensurability". Kuhn took this term from the condition in which "the hypotenuse of an isosceles right triangle is incommensurable with its side ..." such that "there is no common measure" Kuhn, 2000, ps. 35, 60, 189). The condition of "incommensurability" or of two things (like scientific theories) being "incommensurable" means that while these thing can be compared with some degree of precision there is "...no common language within which both [things like scientific theories] could be fully expressed and which could therefore be used in a point-by-point comparison between them" (Kuhn, 2000, p. 189). In this way Kuhnian paradigms (models serving as basis or metaphor for or as examples of scientific theories) are incommensurable (Kuhn, 2000, ps. 162-175). In other words there is no common language to compare two different paradigms (= scientific theories). There is not a common language or common word measure by which the Clementsian biome that consisted only of living things (the biotic community) can be compared completely with the Tanslian ecosystem that included both the biotic community and all the abiotic factors affecting the biotic components. When the prevailing scientific theory (eg. Cleamentsian succession or vegetation development) cannot solve all problems or answer all answers (what Kuhn called "puzzle-solving") arising in conduct of science within the existing body of knowledge a new scientific model (ie. another paradigm) eventually is advanced that can better solve certain of the new "puzzles. This creates subdisciplines or specialities within the more general prevailing discipline much like speciation. Kuhn made frequent use of the Darwinian theory as a metaphor for creation of new disciplines or further specialization from the main tree of a given body of knowledge (Kuhn, 2000, ps. 3, 97, 116-118, 213, 227, 232-233, 307). This development is a scientific revolution or "paradigm shift". |
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| The change in emphasis from vegetation to ecosystems as the object or subject of rapid growth in scientific investigation, the change in fields or subject areas of on-going active research within the general discipline of Ecology, was indeed a “paradigm shift” in Kuhnian theory, a textbook example of a Kuhnian scientific revolution. Tobey (1981, esp. ps. 79-119, 180-190, 196-221 passim) explained the specifics of the Kuhnian paradigm shift from the dominant Clementsian model to the emerging ecological system concept of Tansley. Tobey (1981, ps. 185-190) attributed some, perhaps much, of the decline of the Clementsian vegetation paradigm to Clements’ version of philosophical organicism which Tobey labeled as “the political ideology of plant ecology”. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Tobey (1981) correctly recognized the change from dominance of Plant Ecology by succession theory to emergence of ecosystem theory as a paradigm shift, a scientific revolution.Tobey (1981) incorrectly concluded that paragdigm shifts imply collapse, break-up, or death of the older paradigm. Paradigms are incommensurable. "There is no neutral language into which both of the theories as well as the relevant data may be translated for purposes of comparison". This is why "...comparisons of successive theories with each other and with the world are never sufficient to dicate theory choice". Kuhn, 2000, p. 204). The historic example of scientific revolution to which Kuhn (2000, ps. 15-20, 29-31, 206, 232, 244) repeated returned was comparison of Aristotelian to Newtonian Physics. While the latter replaced the former for certain kinds of "puzzle-solving" this does not mean that Newtonian Physics was superior for all questions or problems arising in the field of Physics or that Aristotelian theory was made obsolete by Newtonian theory. In some "kinds" (branches) of Physics or for certain "jobs" in Physics (perhaps teaching some lessons in Physics) the earlierAristotelian paradigm remains superior. "[T]he ontology of relativistic physics is, in significant respects, more like that of Aristotelian than that of Newtonian physics" (Kuhn, 2000, p. 206). When compared with Aristotle's views of the physical world Newtonian Physics was another, a newer, speciality within Physics or a further subdivision of Physics (a disciplinary "species") that improved "puzzle-solving" for some --but certainly not all-- parts of the now-expanded body of knowledge known as Physics. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|
There is improvement in the solving and solutions of "scientific puzzles" with development of a scientific revolution (formation of another disciplinary "species"), but with this evolution of science there occurs a "communication breakdown" between proponents of different theories or paradigms. This "breakdown" takes place because there is no neutral language to enable complete understanding among members of the different theories or models of doing science. Translations can and must be made into the language of the different theories (paradigms), but this can never be 100% (Kuhn, 1970, ps. 201-204). The reason for this inability to translate between (and thus to compare) paradigms is that meanings of (for) the various "kinds" of things involved change with a changing of theories. An example of this is the changing of the definition of "planet" with coming of the Copernican revolution (Kuhn, 2000, ps. 204-205, 206-207, 312). According to the changed meaning of "planet", the relationship between Earth and Mars and Earth and it's moon changed in going from the Ptolemaic to the Copernican system. In scientific revolutions there is always some overlap, including some shared language, between two successive theories. Kuhn (2000, p. 185-188) expanded his structure of scientific revolutions by elaborating on the concept of a theory-core and an expanded-theory-core as proposed by some of his colleagues. A theory-core "... is a structure that cannot, unlike an expanded core, be abandoned without abandoning the coresponding theory" (Kuhn, 2000, p. 185). Interrelations among organisms would appear to be such a theory-core to both the Clementsian biome and the Tanslian ecosystem, but the theory-core was expanded with the ecosystem beyond living things to include abiotic things. Ecosystem and biome are therefore not synonyms and a complete translation between ecosystem theory (the Tanslian paradigm) and biome theory (culmination of the Clementsian paradigm) is impossible. This is an example of a paradigm shift or a scientific revolution. A parallel example of a paradigm shift in Soil Science was change in classifying soils by the 1938 Zonal-Intrazonal-Azonal System to the Soil Taxonomy System which in oversimplified explanation was a change from a system based on soil formation to one based on chemical and physical features of soils. Soil Taxonomy improved precision of mapping soils, a pedologic illustrate of Kuhn's "puzzle-solving". This scientific revolution in Soil Science eliminated the problematic relationship between soil formation (pedogensis) and identifying and relating taxa of soils. It also eliminated the ability to relate soils to the factors responsible for their formation (and to relate soils to vegetation and climate). With this paradigm shift (change in dominant theory, the theory by which current science is conducted) the names (nouns) by which "things" (in this case, soils) are known or identified changed so much that they are not completely translatable with each other. The Mollisol order of Soil Taxonomy does not coincide completely with the Prairie or Chestnut orders of the 1938 System. The language of successive theories in scientific revolutions are incommensurable. Given the absence of a neutral language complete communication between the two paradigms is impossible. There is an example of the "communication breakdown" (Kuhn, 1970, ps. 201-204) that always accompanies a paradigm shift. This breakdown in communication also occurred between the paradigms (ecological models and theories) of Clements and Tansley. In this case the "breakdown" was so great (and the scientific stature of the two friends who advocated different paradigms so prominent) that it remains a milestone in history of Ecology. With the Clements-Tansley paradigm shift the relationships among plants and animals and their roles or functions (and therefore even designations for plants and animals) changed. In the Tanslian ecosystem plants and animals became producers and consumers such that one part of the interrelationship between them changed from that that of action and co-action in the Clemetsian biome (the preceding paradigm). As such any comparison between these two conceptual or metaphorical views of the "ecological world" must be (and ever remain) incomplete. This is "incommensurability": "... there was no common language within which both could be fully expressed and which could therefore be used in a point-by-point comparison between them" (Kuhn, 2000, p. 189). |
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| The comparison of the two "species" (paradigms) of Physics, Astronomy, Soil Science, and Ecology-- to the extent that paradigms can be compared-- illustrated another central point in Kuhns theory of scientific revolutions. Revolutions (= "paradigm shifts") are "...developmental episodes that introduce new kinds and displace old..." theories. These "revolutions" function "...as transforming episodes in the development or individual sciences", but these are not just "episodes in the development of a single science or sicentific specialty". They are also "...associated with an increase in the number of scientific specialities required for the continued acquisition of scientific knowledge". Such "proliferation of specialities" " ... is apparently prerequisite to the continunig develpment of scientific knowledge" (Kuhn, 2000, p. 250). To gain more knowledge in Ecology the biome concept had to be replaced, at least partially, by the ecosystem concept. A new speciality (Ecosystem Ecology) had to evolve in the metaphorical context of Darwinian evolution or speciation as used by Kuhn..This does not imply-- let alone prove-- that the ecosystem concept came closer to "ecological truth" than did the biome concept or the quasi-organism analogy. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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In the Kuhnian view, scientific revolutions do not mean that each new "species" (specialty or paradigm) takes science successively or progressively closer to the asymptote of scientific truth. More recent scientific theories are superior to earlier or preceding paradigms for solving certain kinds of scientific "puzzles". (Hence development of newer and ever more specialties.) This does not mean, however, "that successive theories grow ever closer to, or approximate more and more closely to, the truth". Such a generalization refers to the ontology not the puzzle-solving capacity of a theory. Recall from Kuhn's example that in some respects Aristotelian Physics was "more like" Relativity Theory than was Newtonian Physics. In going from Aristotle to Newton to Einstein there is improvement in puzzle-solving, but this succession was not necessarily the direction of "ontological development" (Kuhn, 1970, ps. 206-207). While successive stages in the evolutionary development of science result in increased specialization this is without benefit of a "permanent fixed scientific truth" (Kuhn, 1970, ps. 172-173). This same situation (an exact parallel) exist with regard to any comparison between the Clementsian model or paradigm of Dynamic Ecology (Allred and Clements, 1949, p. iii; and the title, Dynamics of Vegetation, of the same) and later specialties or subdivisions like Tanslian Ecosystem Ecology, Plant Population Ecology, or Landscape Ecology. Barbour et al. (1999, p. 208) remarked that in Evolutionary Ecology there have been some models that proposed evolution of entire plant communities. "It is ironic thaat such recent models bring us back full circle to Clementsian ideas of the community as some kind of superorganism..." (Barbour et al., 1999, p. 208). The classical logical-empiricist or logical positivist (=logical positivism or logical empiricism) tradition was a movement in philosophy that tested all statements in reference to experience or the structure of language and sought the unification of the sciences through a common logical language. Logical positivism held that meaningful statements are either analytic or conclusively verifiable or at least confirmable by observation and experiment such that metaphysical theoroes are meaningless. (Merriam-Webster, 1996). Logical empiricism interpreted development of science such that "successive scientific theories provide successively closer approximations to nature" (Kuhn, 2000, p. 205). Kuhn (2000, ps. 205, 217, 226, 286, 306, 309, 310) essentially rejected the logical positivist view of science. A view consistent with Kuhnian theory of scientific revolutions would be that the chronological progression from early Clementsian Community Ecology with the biome as "superorganism" to Tansian Ecosystem Ecology to Landscape Ecology does not yield ever closer approximations to "ecological truth". This sequence of scientific revolutions in Ecology did improve "puzzle" (or problem)-solving capacity for certain things. Most obviously perhaps was inclusion of abiotic factors and their functioning at different spatial or temporal ecological scales. Another example would be improved integration of climate with the biota at scale of ecoregions. Clements' climax and Tansley's ecosystem were perhaps made even more meaningful with development of the latter concept, but it cannot be claimed that each successive modification more closely approached "ecological reality". Nor can it be implied that the most recent "scientific revolution" or "paradigm" replaced earlier ones other than for solving of contemporary ecological "puzzles". Earlier paradigms had previously solved the most pressing "puzzles" of their time just as future paradigms will become dominant to present theories in solving the ecological "puzzles" that are then confronting ecologists. This replacement of paradigms is the essence of "scientific revolutions" and the metaphorical evolution of subdisciplines or specialties. This biological analogy was aptly expressed by Tobey (1981) in his subtitle "The Life Cycle...". |
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| Tobey’s scholarly investigation of the “founding school of American plant ecology”, which was constituted by Clements and his close-working colleagues, and his extremely detailed and well-constructed thesis of a Kuhnian scientific revolution so persuasively argued makes Tobey (1981) highly recommended for any student in Ecology and a “must read” for rangemen or foresters involved with practices based on beliefs that originated from the Clementsian paradigm. The meticulously researched portion on a “network of linked collaborative groups” that constitute what has come to be known as an “invisible college” (Tobey, 1981, chapter 5) was most instructive and intriguing to those interested in the academic lineage of grassland and range ecologists. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Unfortunately,
Tobey (1981) went beyond the Kuhnian paradigm shift to “describe the breakup
of the Clementsian microparadigm”, a “destruction”, which he attributed
to various factors including the great drought of the 1930s and consequent
deterioration of grassland communities, “political and social changes
of the New Deal era”, and Tansley’s loss of “faith” in “Clementsian principles”
(Tobey, 1981, p. 8). In his acknowledgments Tobey (1981, p.ix) admitted
that he may not have convinced everyone “of all of my theses”. Indeed
not. It is one thing to suggest or even prove a shift in emphasis in research
and study in a body of knowledge (ie. changing from one research or instructive
model to another) but quite another to prove that this is due to “failure”,
“breakdown”, or “destruction” of the former model (the paradigm). In fact,
in Kuhnian interpretation a paradigm cannot be said to have been a "failure"
when another disciplinary "species" arises or when comparing
one paradigm (= scientific theory) to another because the two are incommensurable.
There is not a common language between the Clementsian (vegetation devlopment)
and Tanslian (ecosystem) theories. Nor does one Kuhnian paradigm or the
other get us ever nearer to |
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| The fact is that the school of thought and research topics such as plant succession and description of native vegetation that fall under the rubric of what Tobey labeled the Clementsian paradigm were carried on— in fact, invigorated— by the newly emergent profession of Range Management. Many scientists who were products of the “founding school” (some of them graduates from the University of Nebraska and others tracing back indirectly) extended Tobey’s “life cycle” far beyond his obituary notice of the Clementsian paradigm. The active work of such notables as Arthur W. Sampson or E.J. Dyksterhuis and even current range textbook authors like Harold F. Heady is proof that the basic concepts of Clements continued long after the date of 1955 when Tobey alleged that the Clementsian School went extinct. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Where Tobey “went
wrong” in issuing the death notice of the “Clementsian microparadigm”
was in failing to see that when, as he correctly and meticulously charted,
the dominant or active research field of Grassland Ecology moved
into the newly emerging field of Range Management (Tobey, 1980, ps. 143,
145, 148, 150, 153, 219-221) this was merely transfer of Clementsian ecological
investigations into another and a more applied branch of Plant Ecology,
and a branch which Clements had been one of the most influencial founders
of. |
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| It was detailed in a Note in the Range Type section that Clements was probably second only to Arthur Sampson in founding the profession of Range Management and the new discipline of Range Science. Clements was the major player in the “founding school of American Plant Ecology” which Tobey (1981) correctly explained. Clements was also a major founder, probably the second major founder, of the field of Range Management. This second fact, which was traced above, is what Tobey (1981) missed completely. Even if the Clementsian paradigm with its cargo of organicism crashed (as it most certainly did not given re-emergence of fundamental Clementsian concepts as discussed below) there was still the Range Management portion of the Clementsian model that survived as the main body of Clements’ ecological philosophy of vegetation. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| As explained
in the Note in the Range Type section, Range Management was founded by
a relatively small group of men composed of two main elements: 1) on-the-ground
practicing range managers or range administrators primarily of public
range (eg. on National Forests) and 2) plant ecologists (proto-type range
scientists) of which Arthur W. Sampson and Frederic E. Clements were the
two main representatives. Sampson, “Father of Range Management”, was the
more important and influencial in practical application and recognition
of Range Management while Clements provided the theoretical basis of the
newly emergent field in his theory of plant succession and vegetation
development. Application of Clementsian vegetation theory to Range Management
and Forestry came largely through his second ecological monograph, Plant
Indicators (Clements, 1920), that appeared shortly before Sampson
(1923) authored the first “real” range textbook, Range and Pasture
Management. |
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| Tobey (1981)
missed (“glossed over” is more descriptive) the contribution of Plant
Indicators. Tobey (1981, p. 145) was on the right trail when he noted
from his detailed study of cited literature that Plant Indicators
was “frequently cited” in the final, the “exhaustion” or “crisis”, stage
of the life cycle of the “founding school” while the previously “heavily
cited” Plant Succession was not (Tobey, 1981, ps. 144-145, 116).
Tobey (1981) referred to Indicators only that one time and did
not grasp the key role that this companion volume to Plant Succession
played in the development of Range Management. Nor did Tobey (1981) realize
that Range Management was “part and parcel” of the larger, overall Nebraska-based
school of Plant Ecology. |
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| Specifically, Tobey (1981) missed two major points: 1) he did not realize the essential, central function of Clements, especially through Plant Indicators, to creation of Range Management as an agricultural science and 2) he did not realize that Sampson, the principal “sire” of Range Management, was a product of and continued to be influenced by the Clementsian “founding school”. Tobey (1981) did not appreciate the fact that Sampson was such a close follower of Clements’ teaching that “Clementsianism” lived on after the original grassland version of the paradigm was converted into Range Management. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| In fairness to the correct facts found and a thesis well-argued by Tobey (1981), it should be noted that many of the sort of details just presented could not be detected by the kind of analysis Tobey (1981) performed. The tracing of “invisible colleges” by the procedure pioneered by Diana Crane (1972) and the following of connections and ideas by biographical and citation analysis used by Tobey (1981, ps. 112-154 passim, 215-216, 228-250) in reaching his conclusions obviously will work only when the investigator is thoroughly knowledgable with all (at least enough) of the intricate details of the scientific field being investigated. An example of this was when Lucy Braun while writing Deciduous Forests of Eastern North America (1950) corresponded with Clements regarding use of Clementsian concepts (Tobey, 1981, p. 112). Tobey caught that one. Unfortunately he missed most of the more important of those kinds of contacts as between Sampson and Clements for example. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| There were countless connections among the colleagues of the diffused “invisible college” of Range Management and Forestry (probably related fields like Agronomy) that had roots to the Nebraska nucleus of Plant Ecology. These contacts were of the nature that only “insiders” (range scientists, foresters, ecologists, etc.) would be familiar with their details. Tobey (or anybody) could not likely “pull off” this kind of analysis by himself without having been thoroughly versed in the specifics of the body of knowledge or profession under evaluation. For example, the paper by Dyksterhuis (1949) using successional status of key species as basis for range condition/trend analysis has often been regarded as the single most commonly cited work in Range Management, at least from the Journal of Range Management (McClaran, 2000). As explained in the insert Note (Range Type) the idea for the Dyksterhuis (1949) method of analysis can be traced back to Plant Indicators (Clements, 1920), and subsequent research on response of species to disturbances like drought such as conducted by John Weaver and his students at the University of Nebraska. Dyksterhuis earned his Ph. D. from Nebraska. Many more such cases existed that would have shown similar results (eg. the influencial range scientist, author, and teacher L.A. Stoddart, another Nebraska product). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Tobey (1981), or again anybody not familiar with the field of Range Management, could rationally be excused for missing such pivotal details on his own. That excuse failed when the investigator, Tobey in this case, had opportunity to verify findings with knowledgeable colleagues. In his acknowledgements (Tobey, 1981, p. ix) observed that he may not have convinced all the scientists at the University of California, Berkeley “of all of my theses”. No wonder! Had he listened to them or individually sought background information and ideas from them (like he apparently received from others that he acknowledged) Tobey (1981) would not have made the gaffs that he did. Specifically, his errors (most of them anyway) could have been avoided had he open-mindedly corresponded with Drs. Harold H. Biswell, Harold F. Heady, and Arnold M. Schultz of the UC, Berkeley Forestry and Range Management faculty (all Ph. D.s from Nebraska). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Tobey (1981) made several major plunders in the form of faulty assumptions on which his “breakup of the Clementsian microparadigm” depended. One of the most obvious of these to a range scientist was his assertion that, “Range management, as a profession, was largely a product of the Great Drought [the drought of the 1930s] (Tobey, 1981, p. 143). Major erroneous assumption and misreading of the history of Range Management! As pointed out in the Note in the Range Type section, Range Management actually emerged during the period of about 1895 to 1923, the latter year when the first complete textbook of Range Management appeared. Range Management already consisted of enough knowledge to have its own textbook and university courses and curricula before the 1930s. Wasser (1977) established the beginning of actual (professional) Range Management in the year 1895 when Texas stockmen requested research assistance from USDA to halt range deterioration. It was cited above that the first actual publications devoted to Range Management per se were those of Bentley (1898). Wasser (1977) established that the first four-year Range Management curriculum was established in 1916 (Montana State College) and that there were state or state and federal Range Management investigations underway in three states by 1915. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|
Had Tobey (1981) studied the detailed history of Range Management as recorded by Wasser (1977), or even as found in range “principles” textbooks, he would not have carelessly and incorrectly concluded that Range Managaement “was largely a product” of the drought of the 1930s. |
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| Clements (1920) wrote a condensed Range Management text inside of his second monograph, Plant Indicators. Much of his plant succession model in the first monograph (Clements, 1916a) had direct application to Range Management. Both of these and all major texts and references in Range Mangement that existed until after World War II had been written one to two decades before the Great Drought. Barnes (1913) of the Forest Service wrote a textbook-like manual on Range Management before World War I. Range Management came out of Forestry more than any other profession or agricultural field, and Forestry began at turn of the Twentieth Century. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Yes,
the Great Drought was of critical importance as Tobey (1981, chapter 7)
explained in an interesting critique. Yet, the drought only brought to
completion many things that had been in proverbial developmental stages
for years. One case is particular illustrates this. Tobey (1981, p. 220)
wrote: “The drought [of the 1930s] brought forth the Taylor Grazing Act
of 1934, which harnessed grasslands ecology to range management.”. The
first part of that statement is true, but only true to the extent that
the drought (and the Great Depression jointly) was the “last straw” that
finally made possible legislation proposed as far back as John Wesley
Powell’s arid land report (1879) that advocated grazing associations for
proper use of the Public Domain range. The National Livestock Association
endorsed Powell’s suggestions in 1901 as provided for by a bill introduced
into the United States Senate that later became the basis of the Taylor
Grazing Act. In attempts to solve the problem of unregulated grazing use
and consequent overgrazing and deterioration of the Public Domain range
there were no less than 11 bills introduced into either the US Senate
or House of Representatives between 1901 and passage of the final Taylor
Act (Foss, 1960, ps. 39-52). One of the better bills from standpoint of
it’s chance of bringing about proper grazing management was the Kent Grazing
Bill introduced into the US House of Representatives in 1916. This specific
bill was advocated and printed in its entirety by Clements (1920) in Plant
Indicators. |
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| Clearly the Great Drought did not “bring forth” new legislation even though it did “bring forth” new legislative sponsors. It only made possible legislation that had been proposed for at least 30 years, the three decades going back to the beginning of the new profession of Range Management. The drought of the 1930s most certainly did not in any way cause “grasslands ecology” to be “harnessed” to Range Management because that union or conversion had occurred years earlier. The “intellectual shift” from Range Management when “grassland ecology collapsed” (Tobey, 1981, ps. 219-221) was a “realignment” from seeds sown at least as far back as publication of Plant Indicators (Clements, 1920) and the advent of published range research by Sampson beginning about 1913. Although Tobey (1981, p. 286) offered an optional computer printout of 535 titles he did not include one citation of Sampson in his published extensive bibliography that contained numerous sources having no direct relation to Grassland Ecology, Range Management, etc. This is indicative of Tobey’s failure to grasp the early connection of Range Management to the Nebraska school and the fact that the “founding school” was one major source of origin for Range Management. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Finally, Tobey
did not convince this author that “grassland ecology collapsed” at all.
If it did, it reemerged in the Grassland Biome Project of the International
Biological Program three decades this side of the “collapse”. Renewed
interest in North American grasslands also reappeared in scattered groups
of enthusiasts in state conservation agencies and Midwestern teaching
colleges in the 1960s. These “die-hards” whose main focus was on tallgrass,
true, and mixed prairies formed numerous prairie organizations (eg. Missouri
Prairie Foundation). These meet biannually as the North American Prairie
Conference. State-level organizations became popular even in traditional
strongholds of Range Management (eg. Native Prairies Association of Texas). |
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| Most importantly, Grassland Ecology in North America reappeared in its original form in its birthplace. Research on tallgrass prairie ranges and hay meadows has been continuous for decades at land grant universities like University of Nebraska, Kansas State University, and, to lesser extent, others like Oklahoma State University. This was primarily more “applied research” justifiably oriented at problems confronting producers. Beginning in the 1970s with the untiring efforts of visionaries like Dr. Lloyd C. Hulbert of Kansas State, The Nature Conservancy purchased the Konza Prairie in the famed Flint Hills. Scientists on Konza Prairie began what were more basic investigations in structure, function, etc. of prairie ecosystems. Using major funding provided by the National Science Foundation numerous programs at K State began cooperative research with Federal agencies varying from USDA to the National Aeronautics and Space Administration under a Long-Term Ecological Research Program (Knapp et al., 1998). The University of Nebraska School of Biological Sciences and its multidisciplinary Center for Great Plains Study also became involved in research that included Grassland Ecology, including some work at Konza Prairie and new publications that would thrill John Weaver (eg. Joern and Keeler, 1995). Reference to these recent more basic biological types of research was not intended to de-emphasize the continuous Agricultural Experiment Station programs, which in themselves are proof arguing against the assertion that “grassland ecology collapsed”, but rather to illustrate the resurgence of active research much like that conducted by the “founding school of American Plant Ecology”. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| “Full cycle”,
wrote Tobey (1981, p. 221) of his conclusion for the “denouement” of the
“grassland ecology” legacy. And he had it right, though from this author’s
view for the exact opposite conclusion. With the IBP and application of
“Clementsianism” to ecosystem theory as explained later, the Nebraska
“grassland ecology” school came “full cycle”. It recovered as did the
great grasslands themselves (Weaver and Hansen, 1941; Weaver and Albertson,
1944; Weaver, 1954; Weaver and Albertson, 1956). |
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| This is but one example of how Tobey (1981) did an outstanding job of assembling facts and then totally misinterpreted them. In the words of a punchline from a joke made famous by Abraham Lincoln, Tobey “had his facts right but he reached the wrong conclusion". | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|
A second
flawed assumption was: “… the disintegration of normal grasslands science
resulted from internal disillusionment with the microparadigm…” and
“… the emergence of range management within normal science [was an indicator]
of internal disruption in grasslands ecology …”. Nonsense. Grassland
is a major range biome and the fact that Range Management emerged out
of it is only to be expected. It was the major range formation that
the Nebraska school of Ecology had to work with. From what else could
Range Science have emerged? Range Management is to a large extent applied
Plant (specifically Range) Ecology so it is only natural that Range
Management should grow out of Plant Ecology. It says the same thing
worded either way. Tobey’s conclusion about the origin of Range Management
was correct. It was an outgrowth of the Clementsian paradigm and this
was a “success story”, the exact opposite of “breakdown”. It was redirection,
but it was redirection inside the same Clementsian paradigm. It was
rejuvenation of Clementsian Ecology because it allowed the application
of Clements’ theories and concepts to the practice of the agricultural
industries, specifically the grazing or pastoral industry. It was a
“vote of confidence” for the Clements-Weaver school. |
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| The emergence
of Range Management “as a
strong topic within grassland literature” was not “internal disillusionment”
at all. Just the contrary: it was the general acceptance of Clementsian
vegetation theory as the paradigm most apt to provide an initial conceptual basis for a newer knowledge field branching out
from the older base. This redirection within the existing discipline of
Plant Ecology was a natural outgrowth resulting from the application of
the grassland school paradigm as the basis of the new field of Range Management,
a field that Clements had been very influencial in founding. |
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| One commonsense summary explanation for movement of the original Clementsian model from Grassland Ecology studies to the Range Management profession is that as graduates of the now Weaver-Nebraska “founding school” multiplied they had to go somewhere. As with the predominent American frontier, that somewhere was westward. Nebraska could not hold them all. Nor could all the prairie-plains states and provinces whose grassland was continuing to go under to the plow and to agronomic crops. The post- Great Drought-Great Depression-World War II crop of new Weaver-Clementsians moved west into deserts, chaparral, mountain forests, even tundra. In these biomes the original grassland ecology model was no longer the most appropriate. Given that range includes all biomes and that the most plausible promish of professionalism (including employment) lay in all types of natural pasture, Range Management became the latest frontier for the existing Clementsian paradigm. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| With retirement of professors or principal investigators (or death of active emerti) university curricula and research may die or “go dormant” for years so as to complete the “life cycle” of that program. Academia is replete with examples of this. Like professional sports teams, nobody stays on top forever. This, of itself, is not necessarily the same as “breakup” of a disciplinary paradigm or beginning of a scientific revolution. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| In
this author’s opinion, Tobey (1981) greated overstated his case for the
end of Clementsian Ecology and, in fact, failed to prove his allegation
for such demise. The conclusion
reached and argued in this paper is that the Tobey (1981) “thesis” of
“failure” and “destruction” of Clementsian Ecology was wrong, pure and
simple. |
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| Where Tobey, in tracing the historical orgin of applied Plant Ecology, including Range Management, made the wrong turn that took him down a dead end road ending at a nonexistant destination was when he failed to see that Plant Indicators (Clements, 1920) was really the last half of a two-volume treatise on Plant Ecology of which Plant Succession (Clements, 1916a) was the first volume, the theory, and Indicators, the second volume and the practical application of principles laid down in the first. That Indicators was the continuation of Succession was unambigiously stated in Indicators by Clements (1920, p. III): "The present book is intended to be a companion volume to "Plant Succession". The latter was planned to contain several chapters on the applictions of ecology, but these were omitted on account of the lack of space. Chief among these was the consideration of succession as the primary basis for a system of indicator plants, and this has been made the theme of the present treatise". | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Clements' own words prove the fact that these two volumes were actually one book. This was undeniable and commonly realized by rangemen and foresters. Evidence of this plainly stated fact, and an outgrowth of it, was the publication of abridged editions of both volumes as one bound book, entitled Plant Succession and Indicators- A Definitive Edition of Plant Succession and Plant Indicators (Clements, 1928). This "combined and condensed edition" of both original volumes appeared eight years following publication of the unabridged edition of Indicators with "granted permission" and "without responsibility" by the Carnegie Institution of Washington it having "been regarded as a scientific duty to meet the growing demand during the years the books have been out of print ..." (Clements, 1928, p. v). In this same paragraph of the Preface Clements (1928, p. v) offered this explanation: "The two books were designed to be companion volumes, the one dealing with the concepts and principles, the other with the applications of the developmental method. In consequence, it seems entirely appropriate to combine them in a single volume, with a corresponding gain in convenience and economy". The cost of making available both volumes in a single book was omission of five chapters from the original Succession and one chapter from the original Indicators. The latter was the portion describing the formations of western North America, but the applications to Range Management and Forestry were retained. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| The two-in-one abridged edition (Clements, 1928) was reprinted and published in 1963 by Hafner Publishing Company (Arno Press, New York) thereby making the two volumes available to another generation of students. This included any scholars who might choose to write a history of Clementsian Ecology, and provided contemporary evidence to any such historians that Plant Indicators was not a second book and that, in fact, any appraisal of Clementsian thought had to include Plant Succession and Plant Indicators as one book. Given that 1) Clemensian theory was applied to Range Management in both Plant Indicators (Clements, 1920, chapter VI) and the joint, abridged edition of both volumes (Clements, 1928, chapter XV), 2) that research in Range Management under sponsorship by both state and federal agencies began before publication of Plant Succession (Clements, 1916a), Plant Indicators (Clements, 1920), and Succession and Indicators (Clements, 1928), and 3) that practical studies in natural history, ecology, and management of grasslands (as at the University of Nebraska) were coeval in origin with that of Range Management it seemed impossible that the profession of Range Management emerged as a result of "disintigration of normal grasslands science result[ing] from internal disillusionment with the microparadigm [of Clementsian Ecology] as stated by Tobey, 1981, p. 145). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Likewise, it was simply not true, not factual, as Tobey (1981, ps. 147-148) mistakenly alleged that the founding literature of Clementsian Ecology was abandoned after 1928 with "ultimate rejection" of Clementsian theory "after World War II" when concerns of federal scientists "had shifted toward range management" (Tobey, 1981, ps. 149-150). These statements are clearly in error. These conclusions are illogical, if not sheer nonsense, because the dates given by Tobey (1981) are wrong. The chronology of federal publications (primarily United States Department of Agriculture or USDA) devoted to Range Management pre-dated the Twentieth Century (not to mention 1928 let alone 1945) and the most commonly available and cited works of Cleaments (1916a, 1920,1928) were directly related to Range Management, it having been discussed above that the chapter dealing with Grazing Indicators in Plant Indicators (Clements, 1920, 1928) was arguably one of the first Range Management textbooks ever written. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| The fact that Clements' Plant Succession and Plant Indicators was one book, even before the two volumes were combined inside the same cover (Clements, 1928), makes the distinction drawn by Tobey (1981, ps. 144-145) between these two volumes with regard to frequency of citations in the Range Management literature a spurious one. Such distinction was simply an artifact of the format of publication (two printing dates and two separate bindings). Yes, the analytical evaluation of cited literature in this portion (Tobey, 1981, ps. 142-154 passim) was correct, but Tobey drew the wrong inference when he concluded in net effect that the Clementsian microparadigm was replaced due to "decay within" (Tobey, 1981, p. 154) with a resultant shift from the "grassland specialty" to Range Management. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| There are at least three reasons that prove the error of this conclusion. First, any distinction between Clementsian theory and its application is an artificial one because 1) any such differentiation is arbitrary much like that between basic versus applied research (even more so for the fact next explained) and 2) theory and practice in the Clementsian model were a unified whole with both practice and ecological principles mutually dependent on each other (the theoretical perspectives were themselves determined largely by practical questions posed by the newly emerging professions and fields of Range Management, Forestry, and Agronomy). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Second, the fact that the scientific literature more or less stopped citing the Plant Succession portion while continuing to cite the Plant Indicators part (Tobey, 1981, ps.144-145) was due to the fact (a major fact missed by Tobey) that the basic principles in Plant Succession were refined and made more readily accessible to workers in Range Management and Forestry in Clement's influencial (and controversial) article, "Nature and Structure of the Climax", published in The Journal of Ecology (Clements, 1936) and, even more importanly, in the highly influencial textbook, Plant Ecology, (Weaver and Clements, 1929, 1938). There was no longer a need to cite the out-of-print unabridged Plant Succession (Clements, 1916a) because Clements' refinements in climax and community development theory (eg. disturbance climax) presented in the climax paper 20 years later and in the standard-of-it's-field textbook Plant Ecology made the 1916 Succession volume largely obsolete for most citation purposes. Plus, as Clementsian theory became textbook knowledge there was no need to cite certain of the principles ("dogma" to some) introduced in Plant Succession. Citation rate for Plant Succcession (Clements, 1916a), which was assumed by Tobey (1981, ps. 144-145) to be associated with "theoretical or paradigm-oriented" scientists, would naturally have declined sometime after appearance of the more readily available "Climax" paper (Clements, 1936) and Plant Ecology (Weaver and Clements, 1929, 1938). These developments seemed more likely to this author to explain decline in citation rate for Succession than did Tobey's pronouncement of a paradigm shift from Grassland Ecology to Range Management.(The third reason explained in the next poaragraph documented that Range Management was an active field of reserch and innovation before the series of grassland studies arising from the University of Nebraska and it's invisible college or network of collaborators [Tobey, 1981, ps. 133-137]). Tobey's documentation of a steady or even increased citation rate for Plant Indicators was also more likely explainded by availability and relevance of current (as in "up-to-date") publications than by a paradigm shift. Unlike the theoretical portion, Plant Succession (Clements, 1916a, 1928), the more applied or practice-oriented portion of the Clementsian paradigm, Plant Indicators (Clements, 1920, 1928), had only a partial replacement in Plant Ecology (Weaver and Clements, 1929, 1938). The Grazing Indicators chapter in the Plant Indicators portion was the closest thing to an actual textbook in Range Management except for the text by Sampson (1923), and these two publications complemented each as well as the major Range Management publications issued by the federal government (covered immediately below). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Third, and most important of all in this consideration, is the fact stated above that research and development of practices in Range Management preceded the "grassland specialty". As discussed earlier the United States government, largely through USDA, as well as state land grant colleges and universities, through Agricultural Experiment Stations, had conducted research in Range Management (eg. grazing trials, poisonous plants, livestock distribution, revegetation) since the 1890s (eg. Smith, 1899 with investigations begun on mixed prairie range, a grassland cover type, in 1897). "Range Management on the National Forests", USDA Bulletin No. 790, written by Jardine and Anderson (1919) dealt mostly with forest ranges and it had become the "range management bible" before development of the predominantly grassland-oriented Nebraska school under leadership of John Weaver. Arthur Sampson, plant ecologist of the U.S. Forest Service (USDA) and a former Nebraska graduate student, authored a bulletin on range improvement (aimed at forest and mountain meadow ranges) in 1913 and a journal article on revegetation of rangeland in 1914. Obviously research in Range Management pre-dated Clements' monumentally influential monographs. Sampson (1919) wrote "Plant Succession in Range Management", USDA Bulletin No. 791, and it became a shelf companion to Bulletin No. 790. Clearly, Range Management did not emerge after the Nebraska "grassland specialty". Therefore, Tobey was undeniably incorrect when he concluded that "the emergence of range management within normal science" (Tobey, 1981, p. 145), where the normal science period was set by Tobey (1981, p. 143-144) to begin in 1916 (the year Plant Succession was published), was an indicator "of internal disruption in grasslands ecology" (Tobey, 1981, p. 145). Range Management emerged before emergence of the "grassland specialty" not to mention before "internal disruptiion" within such several decades later. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Tobey's conclusion was flawed because 1) Range Management was already an area of active agricultural research by both the US and state governments before the onset of normal science within the Clementsian paradigm and 2) the major portion of the practical or applied part of the Clementsian paradigm was Range Management (in Plant Indicators the Grazing Indicators chapter was larger and of far more relevance to actual practice than either the Agricultural Indicators or the Forest Indicators chapters; in fact, the former chapter was longer than the latter two chapters combined). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Had Tobey (1981) understood that Plant Succession (Clements, 1916a) and Plant Indicators (Clements, 1920) were two volumes of the same book (as when abridged editions of both were bound as one volume in 1928) and if Tobey had grasped the role of the Grazing Indicators chapter on the developing profession of Range Management he could not logically have concluded that Range Management grew out of or replaced the "grasslands specialty" (Tobey, 1981, p. 145). Had this historian grasped the relationship of these two closely related fields and understood the importance and chronological development of that relationship he would not have erroneously concluded that the Grassland Ecology paradigm failed and was replaced by that of Range Management. Tobey (1981) not only got the cart in front of the horse, he mistook the cart for the horse. Again, Range Management emerged before (not after) the specialty of Grassland Ecology. This was the case in both Clements' work (again, especially as Grazing Indicators) and the first actual textbook in Range Management (Sampson, 1923). The presence of a textbook by the 1920s immediately after or coincident with the monographs of Clements (1916a, 1920) indicated that there had to be some body of research and existing literature in Range Management before that time (eg. the research published by Sampson). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| In essence, Grassland Ecology in the United States grew out of the older and more general field of Range Management and not the other way around (ie. Tobey got it backwards: "cart in front of horse"). In America, Grassland Ecology emerged primarily out of the Nebraska school (the "founding school of American plant ecology") especially with John E. Weaver, Clements' most notable co-author, and Weaver's graduate students. Nebraska students (including some who, like Clements, pre-dated Weaver) included Sampson and other well-known names like Jerry Dyksterhuis, G.W. Tomanek, Harold Biswell, Laurie Stoddart, and Harold Heady (to name but a few). All of these distinguished themselves as specialists in Range Management. Most of these workers emphasized grassland range in their research but they also conducted investigations on ranges in forest, shrubland (eg. desert and chaparral), and even tundra biomes. As range, native grazing land, exist on some land of all the terrestrial biomes, Range Management is a larger, broader, and, from some perspectives, a more general or inclusive field than Grassland Ecology. Clements works, in particular his early monographs (Clements, 1916a, 1920) dealt with and provided fundamental concepts for the emerging prominent subfield of Forest Ecology as well as such smaller specialties as Desert Ecology. Some of these principles are still widely accepted and used while others were either rejected or still serve as a basis for scholarly debate (including fierce argument) and model testing. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Kuhnian theory of paradigm shifts does not mean that the previous model which supported the research forefront undergoes “breakup” or “destruction”. It means only that the “scientific frontier” has moved on to newer fields of inquiry within the existing discipline. Neither does a paradigm shift necessarily mean or imply that the previous prevailing paradigm has been proven to be wrong or in error. Take for example vegetation classification. It is no more appropriate to criticize the vegetation development or plant succession model of Clements or the releve model of Braun-Blanquet for omitting habitat or ecosystem components than it is to criticize The Nature Conservancy or Kuchler systems for omitting these factors in classification or mapping of vegetation. As with Clements’ climax hierarchy system, neither The Nature Conservancy USNVC System, Ellenberg and Mueller-Dombois UNESCO scheme, or the Kuchler Potential Natural Vegetation Map included ecosystem study (or, for that matter, much habitat criteria). All any of these systems do in to classify vegetation. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| The change in emphasis from vegetation classification and description to ecosystem structure and function is according to Kuhnian theory a change in dominant research models, hence a scientific revolution, a paradigm shift. It does not mean that ecologists were mistaken to classify vegetation instead of studying trophic levels. Vegetation classification systems are not ecosystem (or landscape) studies any more than simulation models of ecosystems are schemes of vegetation units. These various kinds of ecological studies or programs can be incorporated with each other, at least “in name” and to provide overarching units. The case exemplar was use of biomes as the general unit for ecosystem studies by the International Biological Program, but as Golly (1993) demonstrated this was not very satisfactory and worked to detriment of both of these separate fields of Ecology (ie. it was a case of mixing paradigms). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| It is undeniable that many of the terms, concepts, and most fundamental theories of Vegetation Science which originated with the Anglo-American or English School are in current use. A disproportionately large share of these were contributed by Clements. The biome and climax vegetation are two of these that are still in common use and directly traceable back to Clements and Cowles. Range and forest cover (= dominance) type as an application of the Clementsian climax plant association is another example, but one that can be traced back only indirectly to the Clements-Tansley era. The situation is— and this is the point Tobey (1981) largely missed— that as long as biome, plant succession, climax, cover type, and other basic concepts are useful in the fundamentals of Plant Ecology or in applications thereof (eg. the practice of Range Management and Forestry), Clementsian Ecology is still relevant and cannot be said to have “failed” or “broken down”. Most certainly there was a shift in paradigms or microparadigms in going from Clementsian classification of vegetation and stress on biotic communities to Ecosystem Ecology, but climax vegetation and cover types are concepts currently as useful and widely used by some ecologists as ecosytem. Ecosystem Ecology is an older subdiscipline than Landscape Ecology (as currently defined) and, as mentioned above, Ecosystem Geography is another new ecological field with new ideas that paradoxically harken back to the biome. These newer fields are drawing some scientific endeavor that otherwise might be expended on ecosystem research. Golly (1993) documented weaknesses in IBP ecosystem modeling studies. Do these developments mean “destruction” or “breakdown” of the ecosystem paradigm? No. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| The Kuhnian theory
of scientific revolutions is complex as evidenced by studies of it by
other scientists (eg. Hoyningen-Huene, 1993) or of scientific revolutions
in general (eg. Cohen, 1985). In essence, one paradigm or model, school
of thought, or prevailing body of theory is replaced by another when the
older paradigm cannot provide answers to problems or questions that arise
out of it or its application. Thus Copernican Astronomy emerged (grew
out of) and replaced its preceding Ptolemaic system. This does not mean
that Ptolemaic Astronomy was wrong or irrelevant for all uses but only
that it ccould no longer serve as the model for more advanced or recent
research. Part of it was in error, but it is still in common use for certain
things (Kuhn, 1970, p. 68). The same is true for
Newtonian Physics. Certain Newtonian principles once accepted where
found to be wrong or in error as they were replaced by newer models (Einsteinian
Physics for eg.). Other parts of Newtonian theory are still valid and
are covered in any standard Physics text. In fact any university level
introductory Physics textbook that omitted Newtonian Physics would be
seen as incomplete. Is not the same true of any standard text in Plant
Ecology that omitted Clementsian Ecology? If in the natural resource professions
emphasis shifted from “ecosystem management” to “landscape management”
Landscape Ecology would replace Ecosystem Ecology as a dominant paradigm,
but the ecosystem concept would still be valid for certain uses. The ecosystem
paradigm could not be said to have “failed” or to have undergone “destruction”. |
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| Tobey's (1981) naive and, as seen herein, incorrect allegations of "breakup", "destruction", and "failure" of the Clementsian "microparadigm" were summarily dismissed by Hagen (1992, p. 79-80) when he stated simply "... I am unwilling to accept Tobey's Kuhnian perspective on ". "By presenting the history of ecology as the rise and fall of of paradigms, this perspective places too much emphasis on upon historical discontinuity" (Hagen, 1992, p. 80). The more detailed dismanteling of Tobey's flowed conclusion described herein indicated the specific miscalculations published by Tobey (1981). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| It must be stressed (and remembered) that all accomplished or prominent people are a product, at least a partial product, of the times in which they lived (ie. "the life and times of ..."). As shown throughout this review this was, even if not always obvious, consistently the case for Frederic Edwards Clements. Clements was a product of the science of the age-- the early Twentieth Century-- in which he lived and produced his works. One of the fundamental changes in science (and philosophy of or behind science) of the Twentieth Century was the gradual but continued transition from a perspective that science could be simplified to a foundation of mathematical-like, "clockwork" principles to the growing realization of the role of chance (at least an emphasis on chance) in science. As scientific discoveries increased there was an increasing awareness of apparent aberrations from the "normal", the typical, scheme of things scientific. This story was told summarily in the essay by theoretical physicist, F.D. Peat (2002). | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Life scientists are most familiar with the role of chance in the application of probability theory to Biology, especially the Agricultural Sciences, through statistics. The application of statistics to biological systems through the work of such famous scientists as Sir Ronald Fisher created the science of biometrics or biostatistics used by every graduate student in the life sciences. The role of "chance" or what appears to be "random" happenings (and variation caused by this apparent randomness) in the "working of the world" was expanded in roughly the last quarter of the Twentieth Century. This expansion (perhaps a shift in emphasis on exceptions rather than general rules) had its origin in the pure sciences and their application to such natural systems as those of the atmosphere and oceans. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| One
of the most prominent of these was what became known variously as chaotic
dynamics, chaotic behavior, nonlinear dynamics, chaotic behavior in systems,
chaos theory, or, simply, chaos: "The dynamic evolution that is aperiodic and sensitively dependent on initial conditions... This term takes advantage of the colloquial meaning of chaos as random, unpredictable, and disorderly behavior, but the phenomena given the technical name chaos have an intrinsic feature of determinism and some characteristics of order" (Morris, 1992), "The aperiodic, unpredictable behavior arising in a system extremely sensitive to various initial conditions; phenomena, and that exhibited by chaos, include turbulent fluid flow, low-range weather patterns, and cardiac arrhythmias" (Houghton Mifflin Company, 1993), or "A theory derived from the observation that when the mathematical description of a system includes several nonlinear equations... the future behavior of that system may be unpredictable because of the wide variations that result from its sensitivity to very small differences in initial values supplied to any mathematical model. Chaos was first studied with reference to weather forecasting, but the theory has since been found to have many ecological implications (eg. in studies of predator-prey relations and population dynamics)" (Allaby, 1998). |
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| Students can get the gist of chaos by reading the popularized account of Gleick (1987) and generalized treatments such as those of Holden (1986), Ueda (1992), and Lorenz (1993). These authors included extensive bibliographies including published bibliographies of chaos. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Role of chaos
theory as a major factor in the paradigm shift from the clocklike view
of the universe tracing back to Newtonian Physics to the so-called postmodern
views or interpretations of the scientific disciplines has been variously
expressed as From Clocks to Chaos (Glass and Mackey, 1988) and From Clockwork to Chaos (chapter 6 of Peat, 2002). Such expressions stem from the metaphor of "Newtonian clockwork" (Peat, 2002, p. 117). |
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| Chaos theory appears to be one of the major emerging new perspectives (a paradigm perhaps?) that dulled the luster of scientific certainty that was characteristic of the sciences in the Nineteenth Century through much of the early Twentieth Century. This was the period during which Clements was productive and when the field of Range Management began to emerge. Ecological models such as those of plant succession that followed the machine-like pattern of the pure sciences, especially Physics, were understandably favored and seen as more scientific than those which were less "tidy" or had "noise in the system". The meticulous, precisely ordered ecological schemes in Clements (1916) Plant Succession and his classic paper on the nature and structure of climax (Clements, 1936) fit perfectly with the style or format of the highest science of his day. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Recent models of plant succession such as the state-and-transition model can be related to, and are likely outgrowths of, postmodern "uncertain science" and such theories as chaos. Clements' organicism and his admittedly highly stylized, oversimplified, assembly line-like model of plant succession were products typical of the best science of his time, the age of "clockwork science". | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Strictly speaking, Clements and the entire Clementsian School did deal with chaos, and in the exact disciplines it grew out of: meteorology and climatology. The most obvious example was drought and the University of Nebraska group led by John Weaver. Clements was, as always, ahead of his time and emphasized with obvious effort (and, also as always, with considerable space) climate and its impact on vegetation and its role in development of vegetation. All of this was dynamic (again the contributions of H.C. Cowles and W.M. Davis). This was most conspicuous in Plant Succession (Clements, 1916, esp. ps. 320-343, theories of sun spot activity and drought being the classic example). The difference between Clements' perspective and treatment of atmospheric phenomena (and their influences on vegetation) and that of chaos theory was that Clements tried to explain climatic events and their effects on plant communities as cyclic phenomena (or at least as patterned periodic or episodic phenomena) whereas chaos theory treats of such as being more or less aperiodic or acyclic. At least the theory of chaotic dynamics views system responses (ie "chaotic behavior") as cyclic or periodic at much greater patterns of complexity (eg. mathematical fractals) and, most particularly, as nonlinear. The "clockwork science" of Clements time interpreted natural phenomena as linear and cyclic in simpler geometric patterns. Clements was a top-notch scientist in step with contemporary science and current prevailing theories. As such, Clements' models were relatively simple (certainly not of fractal complexity), linear, and cyclic. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Readers (and critics of Clementsian Ecology) might well ponder this question, "What if instead of his "dynamic ecology" and "dynamic vegetation" Clements had put forth "chaotic ecology" and "chaotic vegetation"? What if he proposed the antithesis of his predictable, inexorable sere to the inevitable climax: a chaotic, unpredictable, never-the-same-twice model? Would "chaotic plant ecology" have application to rangemen and foresters trying to save what remained of native vegetation in a time when the rank and file of man was being driven to destroy the same through the forces of hunger, economic disintegration and revolution, ignorance, and greed? If vegetation was an unknowable biological wild card what incentive would there have been to try to manage it? This author suggest that the alternative to the certainty of the deterministic Clementsian model would have delayed acceptance and application of Vegetation Science to emerging professions like Range Management and Forestry. Clements' deterministic path to a definite terminus that was capable of being modified, even enhanced or expedited, by human coaction was the right prescription for its time. It furnished faith in the future for those trying desperately to save what remained of former bountiful forests, grasslands, and desert ranges. Without the certain (over-certain perhaps) clock-like science along the lines of the Clementsian model there would have been much less impetus for early conservationists and the disciples of Progress and the "gospel of efficiency" to have believed in and applied the principles of scientific management to natural resources, action that certainly saved so much of them for future generations. | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
In
sum then, any argument that controversial aspects of the Clementsian model
(and again organicism is probably the most controversial) coupled with
“general old age” lead to “destruction” of this model must be seen as
mistaken and even greatly flawed. As long as biomes (or ecoregions), cover
types, and range sites remain in use Clementsian Ecology remains relevant
(ie. “alive and well”).
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