ECOLOGY OF PRIMARY TERRESTRIAL CONSUMERS 255
estimate the effi ciency with which these processes are carried
out, as for example
assimilation efficiency
calories assimilated
calories ingeste
dd
growth efficiency
calories in growth
calories ingested
yield
eefficiency
calories to man (or other exploiter)
calories ingest
eed
These and other effi ciencies provide the means for compar-
ing different trophic levels or other ecological units with
respect to their functional roles in the ecosystem. For pri-
mary consumers, the ratio
calories consumed by herbivore population
calories of available plaant food
measures their food-chain effi ciency, while the ratio
calories of herbivores consumed by carnivores
calories of plant foodd consumed by herbivores
measures their effi ciency of energy transfer.
DIVERSITY OF PRIMARY CONSUMERS
All parts of plants—leaves, buds, fl owers and their products
(seeds, pollen, nectar), stems, sap, roots, bark and wood—
are eaten by primary consumers, who have evolved a great
diversity of life form and habits in response to their food.
Large grazers and browsers, such as elephants and deer, can
ingest plant tissue in bulk, but others are specialized to par-
ticular products, e.g., the mylabrid weevils that feed on beans
and peas, and the sap-sucking aphids and leaf-hoppers. The
specialization may extend to particular kinds of plants; the
Australian koala “bear,” for example, is limited to leaves of
Eucalyptus, and the larva of the swallowtail butterfl y Papilio
marcellus feeds exclusively on the foliage of the prickly ash
( Zanthoxylua ). Much less is known of the food habits of
detritus-feeders, which never attain the large size of some
grazers, but Petrusewicz and Macfadyen (1970) point out that
“remarkably few species restrict their diets at all narrowly.”
All of the principal phyla of land animals have developed
forms which are partly or entirely herbivorous, and it is likely
that the majority of terrestrial heterotrophic species are pri-
mary consumers. About half of the known kinds of insects
are plant-eaters (Brues, 1946), and in some habitats the pro-
portion may be considerably higher: Menhinick (1967) found
that herbivores made up about 80% of the insect species of a
bush clover ( Lespedeza ) stand in South Carolina, and Evans
and Murdoch (1968) reported that 85% of approximately 1500
insect species encountered on a 30-year-old abandoned field in
Michigan were herbivorous. With such diversity, it is unlikely
that any species of plant has escaped exploitation by herbi-
vores. Indeed, most plants are host to a wide range of consum-
ers; for example, at least 227 species of herbivorous insects
are known to be associated with the oaks ( Quercus robur and
Q. petraea ) of British woodlands (Elton, 1966, 197).
The most important insect consumers of live veg-
etation belong to the orders Orthoptera (grasshoppers),
Hemiptera (true bugs), Homoptera (leaf-hoppers, aphids,
scales), Coleoptera (beetles), Lepidoptera (moths, butter-
flies), Diptera (flies), and Hymenoptera (bees, wasps, ants).
Insects as a group share dominance as herbivores with the
mammals, including such larger types as horses, pigs, deer,
antelope, goats, sheep and cattle, and such smaller ones as
hares, rabbits, squirrels, marmots, voles and lemmings. (In
tropical regions, various monkeys and apes are also impor-
tant herbivores, as are fruit-eating and nectarivorous bats.)
There are significant herbivores among terrestrial birds,
e.g., the Galliformes (grouse, quail, pheasants) and the “spe-
cialist” seed-eating finches and sparrows, the fruit-eating
parrots, and the nectar-sucking hummingbirds, and among
land mollusks, such as the “garden” snails and slugs.
Much less is known of the herbivores which feed on
roots, underground stems, and other living plant parts in the
soil. Studies by Bornebusch (1930), Van der Drift (1951),
Cragg (1961) and Macfadyen (1961) indicate that the most
important groups of herbivores in north temperate grassland
and forest soils are the parasitic nematode worms, the molluscs,
and the larvae of Diptera, Coleoptera, and Lepidoptera. They
occur in close association with other primary consumers, the
detritus feeders, which include the Oligochaeta (earthworms
and enchytraeid worms), Isopoda (wood lice), Diplopoda (mil-
lipedes), free-living Nematoda, Collembola (spring tails), and
Acari (mites). The mechanical comminution of dead matter by
these organisms provides a substrate of small particles which
can be more easily attacked by fungi, protozoa, bacteria and
other microorganisms (Phillipson, 1966).
MEASUREMENT OF PRIMARY CONSUMPTION
The measurement of primary consumption involves the
assessment, in terms of number of individuals, biomass,
and energy equivalence, of the quantity of herbivorous ani-
mals present or produced over a period of time, the ener-
getic cost of producing and maintaining that product, and
the fate of the matter and energy that becomes incorporated
in herbivore tissue. A detailed account of methods and tech-
niques employed for these purposes is beyond the scope of
this article, but a brief treatment is presented below.
The mobility, abundance, and small size of many primary
consumers make it difficult to assess their numbers. Total
counts or censuses, as of large mammals by aerial photog-
raphy (Parker, 1971) or of small ones by intensive trapping
(Gliwicz et al., 1968), can only rarely be achieved, and it is
general practice to rely on sample collections (e.g., Wiegert,
1964, 1965). The marking of individual organisms for subse-
quent recapture has been employed to estimate population size
in such herbivores as grasshoppers (Nakamura et al., 1971),
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