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<br />
<br />Primarily because of its mid-continent location, the
<br />Basin experiences weather that is known tor its fluctuations
<br />and extremes. Averages are misleading for seldom does aver-
<br />age weather actually occur. Instead, weather tends to fluctuate
<br />widely around the annual averages, with the occurrence and
<br />the degree of fluctuations being unpredictable. Winters are re-
<br />latively long and cold; summers are fair and hot; spring is cool,
<br />moist, and windy; autumn ;s cool, dry, and windy.
<br />
<br />Normal annual precipitation varies from west to east in
<br />the Basin, averaging over 35 inches in the Rocky Mountains of
<br />the western boundary, about 14 inches on the Great Plains,
<br />about 26 inches on the Central Lowlands, and over 36 inches
<br />in the Ozark Highlands. Figure 4 shows normal annual precipi-
<br />tation for the period 1931- 1960. About 70 percent of the pre-
<br />cipitation occurs as rainfall during the growing season.
<br />
<br />One of the climatic factors of great importance because
<br />of the agricultural activity in the Basin is the length of the frost-
<br />free period. The definition of the frost-free period is the average
<br />number of days each year between the last freezing tempera-
<br />ture in the spring and the first frost in the autumn. While the
<br />frost-free period does not completely define the growing sea-
<br />son for all crops and grasses, it is a general indicator of the
<br />most favorable period. The length of the frost-free period in the
<br />Basin is about 30 days in the higher elevations of the Rocky
<br />Mountains, about 140 days on the Great Plains, and about 180
<br />days in the Ozark Highlands.
<br />
<br />The subbasin descriptions include a discussion of their
<br />average winter and summer temperature ranges..
<br />
<br />Environmental Resources
<br />
<br />TERRESTRIAL BIOLOGICAL RESOURCES
<br />
<br />Ecosystems <if the Missouri River Basin originally were
<br />dominated by various grassland types in the pra[ries and plains
<br />region, and by forests, shrublands, mountain grasslands, and
<br />alpine tundra in the mountainous regions, Gallery forests, with
<br />most biotic diversity in the Middle Missouri and Lower Missouri
<br />subbasins, developed along the major rivers and streams. In
<br />recent times, much of the various grasslands types of the
<br />plainS and prairie region have been converted to cropland
<br />wherever favorable soils, topography and climate exist, al-
<br />though natural grasslands of sizable acreages do persist in
<br />several States in areas of less favorable topography, substrate,
<br />or climate. The shrubland, woodland, and forest iand of the
<br />mountains have not been subjected to intensive disturbances
<br />and retain more of the natural characteristics. River bottomland
<br />forests in the prairies and plains have been eliminated or have
<br />deteriorated in many parts of the Basin, but many still afford
<br />key habitat for native plants and animals. The agricultural lands
<br />now support a mixed array of some of the native biota, having
<br />broad ecological tolerances, and a host of tolerant or cultural
<br />exotics Including herbs, shrubs, trees, insects, birds, and
<br />mammals. Occasionally, populations of some native species
<br />explode, and the species becomes a new pest. This is related
<br />
<br />to their ability to extract energy and raw material from new cul-
<br />tural environments at an accelerated rate due to lack of checks
<br />and balances. However, other native populations typically have
<br />more narrow ecological requirements. and often decline or be-
<br />come extinct regionally.
<br />
<br />The native terrestrial biota in the Missouri River Basin
<br />have been exposed to a succession of changing environments
<br />in the geological past, and only a few known endemic species
<br />have survived the extremes of the Pleistocene epoch. During
<br />this time successive gla~jers scoured much of the mountains
<br />and caused a direct or indirect deposition or reassortment of
<br />massive amounts of sediment. Affected biota were forced to
<br />migrate or become extinct. Biotic relicts of that period still per-
<br />sist in some areas of the Basin, and populations contain poten-
<br />tially important genetic information. In historical periods this
<br />array of biota has been exposed to stresses differing in type or
<br />extent including new chemicals, artificial lights and noise.
<br />megadisturbance of substrate or soils, animals, and direct ex-
<br />posure to large human populations. As a result, some species
<br />have become extinct, still others have lost most of their habitat,
<br />while Qthers have been declining over broad areas. Only a
<br />comparatively few species have benefited from special conser-
<br />vation measures. Fortunately, ecosystems in the Basin still are
<br />of sufficient size and integrity to support large populations of
<br />the native flora and fauna, and, in addition, allow for sizable
<br />sustainable harvests. The economic and social worth of this
<br />resOurce in the past, however, has not been fully understood or
<br />appreciated within an economic system where short-term
<br />exploitation of nonrenewable resources has often received
<br />priority over conservation and management of less marketable
<br />renewable resources.
<br />
<br />
<br />American buffalo on South Daleota range
<br />
<br />Terrestrial big game species, such as moose, elk. deer,
<br />Rocky Mountain goats, big horn sheep, and grizzly and black
<br />bears, continue to be in much demand in the Basin by both
<br />residents and nonresidents, and are in short supply in most
<br />States with the exception of Wyoming, where surplus popula-
<br />tions of pronghorn antelope occur. In Montana, a State with the
<br />highest overall population of big game resources in the con-
<br />tiguous 48 States, the sale of nonresident licenses leads the
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