Acta Biotheoretica XXIV (3-4) : IOO-lO7 (I975)
NICHE, HABITAT, AND RELATED ECOLOGICAL
CONCEPTS
by
M. REJMANEK and J. JENIK
Department of Botany, Caroline University, Praha
Botanical Institute, Czechoslovak Academy of Sciences, Prfihonice
(Received 27-VIII-I974; revised 2I-I-I975)
SUMMARY
DARWIN'S phrase "place in natural economy", and SPENCER'Sterm "correspond-
ence" can be regarded as first attempts to express the organism-environment
relationships. The same concept has more recently been approached from the
point of view of (I) life-form, (2) external activities, and (3) habitat. Though all
these points are interlocking, they have been stressed differently in the writings
of American and European ecologists. It is proposed that the term "niche" would
be most useful and rational if applied to the total of relationships between a living
organism (population, species) and its complete environment, both biotic and
abiotic.
INTRODUCTION
T h e concepts of " n i c h e " and " h a b i t a t " occur v e r y f r e q u e n t l y in current
ecological literature, and h a v e become an i m p o r t a n t tool in the develop-
m e n t of ecological theory. N u m e r o u s a t t e m p t s to classify and re-define
t h e m h a v e been made, particularly in American journals. The recent
paper b y WHITTAKER, LEVlN & ROOT (1973) was a m a j o r contribution
in exploring this problem, and the present p a p e r is in p a r t a response to
some of the ideas expressed in t h a t work. Many E u r o p e a n ecologists now
realise t h a t " n i c h e " , after all, is a useful t e r m in the ecological vocabulary,
although E u r o p e a n ecology m a n a g e d to do w i t h o u t it until v e r y recently.
HISTORICAL NOTES
The history of the concept and definition of the t e r m " n i c h e " has been
described b y SAVACE (I958), UDVARDY (I959), WOENSCHER (I969),
VANDER•EER (1972) and others. Some points in the old E u r o p e a n litera-
t u r e are particularly interesting in the d e v e l o p m e n t of the idea of organ-
i s m - e n v i r o n m e n t links. F r o m the v e r y beginning this idea of relationships
between a living organism and its surroundings, was coupled with the
basic biological concept of "species". DARWIN (1859) refers to species
"filling nearly the same place in the n a t u r a l e c o n o m y of the l a n d " (ot). cit.,
SOME ECOLOGICAL CONCEPTS IOl
p. 173; see also p. 76 and 81) and to "a place in the natural polity of the
country" (off. cit., p. 177-178 ). It seems that DARWIN followed LINNAEUS'
term "Oeconomia Naturae" which was commonly used, in the pre-
Haeckelian period, for a category of interrelationships in nature. Taking
into account the context in which these phrases occur, we m a y assume
that DARWIN'S "place in natural economy" contained in essence the
features later united with the term "niche" as variously defined b y
GRINNEL (I917), ELrON (1927), HUTCHINSON (1958) and other proponents
of these views.
Tile need for a precise term expressing close organism-environment
relationships can be traced back to the synthetic philosophy of SPENCER
(1898, ed. 1915). This book contains a separate chapter on "The Cor-
respondence Between Life and Its Circumstances" (op. cit., p. 91-1oo).
For the system of mutual relations between living organisms and their
environment, SPENCER proposed the term "correspondence". He was
aware of verbal imperfection in defining the interrelationships (op. cit.,
P. 97), and wrote as follows: " . . . we have no word sufficiently general to
comprehend all forms of this relation between the organism and its
medium, and yet sufficiently specific to convey an adequate idea of the
relation; and the word correspondence seems the least objectionable"
(o25. cit., p. 98). A study of the relevant chapter suggests that SPENCER'S
"correspondence" involved tile complexity and dynamics attributed to
the modern concept of "niche".
THREE APPROACHES
A complete understanding of organism-environment link has so far
proved extremely difficult. It can be looked at and analyzed from many
points of view, which are affected considerably by the w a y conceptual
systems have developed in various countries; b y differences between
particular biological sciences (especially in zoology and botany); and
partly b y the goal of the research. Three aspects have appeared most
frequently: (I) that of the morphological features of the organism (or
species) itself 1) ; (2) from the point of view of the external activities of
the organism (species) itself; and lastly (3) from a consideration of opera-
tional environment. Some comments on these three approaches will be made.
1) H an organism is considered, we have in mind factual data on a single pheno-
type; in case of the population or species, average data are concerned referring to
more or less statistically defined distribution of actual data in relation to the mean
representative. The same distinction can be applied if environment of an individual,
population or species is concerned (see MAELZEI~1965).
102 M. REJMXNEK AND J. JENfK
(1) A marked feature of the organism-environment link is the morpho-
logical features of the organism. In the majority of cases, morphologicM
characteristics are the only information available on the biology of the
species being studied. Many of these show obvious adaptive and functional
significance, which make them a suitable basis for the classification of
life-forms, such as that introduced by WARMING (1884) and RAUNKIAER
(1905) into botany, and by REMA~E (1943) into zoology. In a compre-
hensive study of life-forms, GAMS (1918) first expressed clearly the idea
that life-forms of both plants and animals can be the key to comprehen-
sion of ecological relationships; this can be seen in his chapter "Life-forms
as an expression of entire ecology" (@. ciZ., p. 311). It was GAMS' work
which led BALOGH (1958, p. 79) to claim the terms "niche" and "life
form" are synonymous, and to point out the far-reaching parallels in
terminology within American and European ecological literature.
(2) Understandably enough, zoologists have mainly emphasized organ-
ism-environment relationships from the point of view of the activities
and responses of the organism, and this has led to the notion of "niche"
as defined by ELTON (1927, p. 64), CLARKE (1954, p. 468), SAVAGE (1958)
and 0DUM (1964, p. 27). The last author has defined the niche as the
status (profession or role) of an organism in its community or ecosystem,
which Call be estimated according to various criteria. A frequent result
of this approach is the classification of organisms according to their food
requirements (herbivores, carnivores, necrophages, omnivores, etc.). The
given two approaches, viz. through the life-forms and external activities,
can be considered as special case of "form-function problem" (@ JEUI~EN
1958).
(3) The third approach towards organism-environment interaction is
that from a consideration of the surrounding matter and energy, i. e.
operational environment in the sense of MASON & LANGENttEIM (1957)
and SPONER (1973). The older terms of "habitat", "Standort", "Lebens-
ort", "MeCTOO6~TaH~e" etc. frequently contained ideas pertaining to
the concept of the organism-environment complex. The newer term
"niche" has naturally often overlapped the older definitions. This in-
terpretation is already apparent in the work of GRItqNEL (1924, p. 227).
The elaborate notion of HVTCt~INSO~ (1958) presenting "niche" as
n-dimensional hypervolume of environmental variables, is also close to the
habitat concept. Consequently, most European ecologists would regard
the use of the term "niche" in this sense as superfluous. However, in a
later work HUTCHI?;SON (e. g. 1965, p. 32) also includes in his hyperspace
"a relevant variable in the life of a species of organism", and gives the
SOME ECOLOGICAL CONCEPTS lO3
life-form of two African rhinoceros species as an example of niche diversi-
fication (@. cit., p. 33-35) 2). LEVlNS (1965, p. 326), following HUTCmN-
SON'S idea, defines niche as "a fitness measure on an environmental
space".
COMPLEXITY AND D E F I N I T I O N OF NICHE
Though the three approaches already mentioned m a y appear very
different, they are in fact related and can often be deduced from each
other, as can be seen from the following diagram:
Morphological f e a t u r e s
/
Operational environment
(life-form)
A c t i v i t i e s and r e s p o n s e s
<
(habitat) > (behaviour)
For example, knowing that the food of a certain animal is found only in
the soil (a type of habitat), we can deduce that this animal will gain its
food by digging (its behaviour); in order to dig, the animal must be
adequately adapted morphologically (its life-form). Another example: if
a solid rock provides a suitable substratum for growth of a lichen (feature
of the environment), the lichen must possess substances which can desinte-
grate the substratum (external activities), and also develop a cortical
thallus enabling maximum contact with the substratum (life-form).
These deductions can also be made in the reverse direction and m a n y
examples of this type of reasoning can be found in comprehensive aute-
cological monographs. These deductions, however, need not be always
unambiguous. In order to comprehend the totality of organism-environ-
ment relationships, simultaneous utilisation of all three approaches seems
to be desirable.
As seen above the concept of "organism-environment linkage" is a
o) This w a y of niche definition appears to be less ambiguous for A m e r i c a n authors
who s p o n t a n e o u s l y assume t h a t " h a b i t a t refers to some particular c o m b i n a t i o n
of e n v i r o n m e n t a l characteristics, t a k i n g into account their n o r m a l t e m p o r a l fluctua-
tions, as t h e y are found in a p a r t i c u l a r geographical l o c a t i o n " (MAGuIRE 1973).
M a n y E u r o p e a n authors t e n d to use the " h a b i t a t " t e r m as general t e r m for ecologi-
cal conditions of a species, s y n o n y m o u s to the G e r m a n " S t a n d o r t " which f r e q u e n t l y
express t h e t o t a l of soil, ar and o t h e r ecological conditions, w i t h o u t
p a r t i c u l a r reference to geographical location (see WALTER 1960).
Io4 M. REJMfiNEK AND J. JENiK
very complex phenomenon which definitely requires a distinctive and
unambiguous term. The word "niche" could be used in this connection,
but the problem remains of defining its limits. For example, WHITTAKER
(1970, 1972 ) and WmTTAKER et al. (1973) recommend calling our No. 2
approach the niche, and limit its meaning to "intracommunity factors"
in contrast to the "intercommunity factors" referring to habitat. Regard-
less to these suggestions, perhaps the most useful and rational definition
in the setting of ecological theory would be to describe the niche as the
total of relationships between a living organism (~@ulation, species) and
its complete environment, both biotic and abiotic. As suggested by
HUTCI~IINSON, one can distinguish "a realised niche" (referring to a
specific individual organism or population in one habitat or succession
of habitats), and "a fundamental niche" (referring to the total number
of potential niches, i. e. all possible relationships in which representatives
of the population (or species) can exist).
This broad definition is in agreement with BOCK & WAI~LERT (I965) ,
who introduced a useful concept of the "synerg" for a single component
of the "niche"; in the majority of cases, niche was illustrated in two-
dimensional diagrams only by two synergs (WARBURG 1965, Fig. I; etc.).
A synerg has been defined as a link between the organism and its environ-
ment formed by one single selection force of the operational environ-
ment and one biological role of an organism. Then the niche of an organ-
ism can be defined as the sum of all its synergs (BOCK & WAItLERT 1965,
p. 281-2). Other recent definitions also emphasize the complementary
significance of both the environment and the response of the organism,
e.g. WUENSCI~ER (1969), MAYR (1970, p. 42I), MAGUIRE (1973) and
E?~ILEN (1973, p. 210-14). It is clear that this broad meaning of "niche"
is also in agreement with the ideas of DARWIN and SPENCER quoted above.
There is an urgent need for quantification of ecological concepts,
including that of "niche". VAXDER~IEER (1972, p. 108) remarks:
" . . . quantification is what niche theory is all about". The mentioned
authors has used the competition model as a starting point. LEVlNS
(1968) points out that any satisfactory theory of the niche must allow:
(I) a measure of niche breadth, (2) a measure of niche dimension, (3) a
measure of niche overlap between species, and (4) a method of using the
niche model to explain species diversity. SHUGART & PATTEN (1972)
suggested the general method for niche quantification from the point of
view of habitat selection. Other papers streamlined to the quantification
of certain parts of niche were presented by COLWELL & FUTUYMA (I97I),
GALLOPIN (I972), GREEN (I97I), PIANKA (I969), and PIELOIJ (1972).
SOME E C O L O G I C A L CONCEPTS IO5
However, a comprehensive analysis of the total biological mealr of
niche should precede this quantification, and this paper is an attempt to
contribute towards this goal.
CONCLUDING REMARKS
In the sense defined here, "niche" may serve as a fundamental ecologi-
cal concept of similar importance to "ecosystem". One might even define
ecology as the "science of niches and ecosystems". For this purpose,
however, we need to know the mutual relationships of these terms. Ac-
cepting the broad definition of DALE (1970 , p. 3) that "an ecosystem is a
system open for at least one property, in which at least one of the entities
is classed as living", and assuming that the ecosystem concept is concerned
with function and not merely components, we can take the niche of an
individual organism as the most elementary ecosystem. But in m a n y
cases, "niche" will be connected with the concept of "species". At this
level, "niche" represents a quite different concept from "ecosystem",
since the space occupied by a species population is often discontinuous,
and individual members of the population frequently migrate within
various ecosystems. On the other hand all complex ecosystems can be
considered as systems of realised population niches and/or realised niches
of individual organisms.
The proposed broad definition of niche seems to be appropriate be-
cause of its possible restriction to one or several synergs (se~su BOCK &
WAHLERT 1965) including the "intracommunity aspect" of WHITTAKER
et al. (1973). Thus it is always possible to specify the type of niche by
describing various attributes, e. g. food niche, habitat niche, time niche,
etc. (see ALLEE et al. 1949; PIANKA 1969; etc.).
Finally, a comment should be made on the term "ecotope" proposed
by WHITTAKER et al. (1973) for Nos. 2 and 3 aspects of niche (see above)
which cover both the role of a species in a given community and its
habitat. In the European literature there are two prevailing meanings of
this term: "landscape element" (Sc~IMITH/3SEN 1961, p. 78; TROLl. 1968,
p. 15) and "abiotic part of the environment" (LAVRENKO1959, p. 35;
SCHENNIKOV 1964, p. 27; ZLATNIKet al. 1973, p. 40). Though unfortunate,
this double sense is well established in the scientific vocabulary, and it
would be rather confusing to introduce a third meaning for the same word.
ACKNOWLEDGEMENTS
The authors are indebted to Prof. E. HADA~, Prague, for valuable
suggestions concerning DARWIN'S work, and Dr. and Mrs. K . A .
LONGMAN,Edinburgh, for linguistic revision of the manuscript.
lO6 M. REJMfi~NEK AND J. JENiK
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