Upload
others
View
0
Download
0
Embed Size (px)
Citation preview
Global grasslands: comparing the U.S. Northwestern Glaciated Plains and the Mongolian-
Manchurian Steppe
Brooke Jacobson
University of Idaho
Moscow, ID 83843
406-839-4706
Keyword : Northwestern Glaciated Plain, temperate, glaciated, Mongolian-Manchurian, arid
Reference: Jacobson, B.A. 2012. Global grasslands: comparing the U.S. Northwestern
Glaciated Plains and the Mongolian-Manchurian Steppe. REM 452.
Figure 1: The Norwest Glaciated Plains,
highlighted in orange, and the Missouri
Coteau, depicted in blue. Adapted from
WWF, 2012.
The Northwestern Glaciated Plain stretches from the southern regions of Alberta and
Saskatchewan, through north-eastern Montana,
and follows the Missouri River south through
North and South Dakota into a small portion of
Nebraska (Figure 1). The eastern edge of this area,
the Missouri Coteau, is also considered part of this
ecoregion for the purposes of this paper. This
grassland-steppe ecoregion covers roughly
160,000 km2 (USGS 2011) in the United States
and 250, 000 km2
in its Canadian range (Vance
1997). It is bordered to the west by the Rocky
Mountains and to the north by the Aspen
Woodlands and Boreal Forest. The land is not as wet and flat as the Northern Glaciated Plains to
the east, or as irregular topographically as the Northwestern Great Plains that border this area to
the south (EPA 2012). The Northwestern Glaciated Plains has a semiarid climate that exhibits
warm to hot summers with frigid winters. Temperatures range from 3 to 7 ºC, and decline with
elevation and northern latitude. Elevation in the ecoregion ranges from 610 to 1839 m (USGS
2011). Precipitation is low in the in the region, and yearly averages vary from 250 to 380 mm
(McNab and Avers 1994). The growing season is this ecoregion lasts roughly 100 - 130 days.
The Northwestern Glaciated plain lie in the rain shadow of the Rocky Mountains, and
consequently the weather patterns are largely controlled by storm systems from the Gulf of
Mexico. Most precipitation falls in the spring and early summer, and the region receives the
majority its moisture in the months of May and June (USGS 2011). In the northern reaches of
Northwestern Glaciated
Plains
Ecoregion
Figure 2: Rolling glaciated Canadian
grassland. From Robert T. Coupland 1961.
this ecoregion, up to 20% of the annual precipitation may fall in the form of snow (USFS 2011).
High winds are also a factor that have a large influence on climate and exacerbate
evapotranspiration. Some areas have an annual moisture deficit of 30 cm per year or more
(Yansa 1998) Due to this variable weather pattern and its semiarid climate, the area is subject to
drought (USGS 2011).
Topography is variable within the Northwestern Glaciated Plain. Mountains in the
Montana portion of the ecoregion formed from volcanic activity and were influences by glacial
movement (Stewart and Kantrud 1972). Physiognomic features in the eastern Missouri Plateau
differ from areas in greatly from these mountain outcrops. The Missouri Plateau, also referred to
as the Coteau du Missouri or “hills of the Missouri”, is the rolling grassland region along the
Missouri River (Kruse and Piehl 1986). Its northern range includes the grassland region in
southern Canada known as Palliser’s Triangle.
Despite the varying topography,
the Northwestern Glaciated Plains are
predominantly hilly to flat grassland
prairies with occasional mountain outcrops
and playas (Figure 2). These playa areas,
referred to as prairie potholes, occur in
both the Canadian and U.S. portions of the
plain. These water bodies, which may be
ephemeral or permanent, are shallow depressions formed after the melting glacial ice buried
beneath deposited sediments during the Pleistocene glaciations. The glacial till that is covers the
land in this area is comprised of more than 50% silt and clay, making these soils fertile, but
sometimes impermeable where they have formed aquitards -- land formations which restrict
groundwater permeability (Van der Kamp and Hayashi 1998). Gneiss, granite, dolomite,
quartzite, and limestone comprise the glacial till in the Couteau du Missouri, often giving the
land a stony appearance. The glacial parent material of the plain, much of it containing
carbonates and pyrite, are the source for much of the salts in prairie wetlands (Van der Kamp and
Hayashi 2009). Many of these potholes are ephemeral due to the hot summer climate. The
wetland and pothole areas of the Northwestern Glaciated Plains serve as important breeding
habitat for of dabbling ducks, Anas spp. (Krapu 2000).
According to an extensive survey of the region by Stewart and Kantrud (1972), wetland
vegetation in the Northwestern Glaciated Plain includes Ditichlis stricta, Hordeum Jubatum,
Carex brevior, Juncus balticus, and Carex antherodes. Other species including Typha spp.,
Symphoricarpos occidentalis, and Rosa woodsii also occur, as well as Salix spp. and Populus
spp. Salinity is the main determinant of the species composition of these wetlands (Neill 1993,
Stewart and Kantrud 1972).
Dominant grasses include in the Northwestern Glaciated Plain include Hesperostipa
comata, Bouteloua gracilis, Hesperostipa spartea, Agropyron smithii, and Koeleria macrantha
(Brown 1993, Coupland 1961, Stewart and Kantrud 1972). Woody species and forbs are less
common in the dry grasslands and include Salix spp. and Populus spp.
Fire and drought have historically been determinants of natural vegetation in the region
(Taylor 2011). Since the arrival of Europeans around 100 years ago, conversion of native
rangeland to agriculture has been an ongoing phenomenon in this region. Irrigation is difficult in
the drier areas, but access to ground water by has opened up more arid land in the area. Drainage
of the Prairie Pothole region and conversion to cropland has also changed the hydrology and
habitat functions of the area. Fossil fuel extraction has also had an impact on the Northern
Glaciated Plain. Oil and natural gas development began in the mid-nineteen-hundreds, and
continued mining of the Bakken formation have also changed the landscape of the Northwestern
Glaciated Plains in eastern Montana and western North Dakota.
British explorer Captain Palliser explored the region that is now southern Canada in the
mid nineteenth century and reported that the area was unlikely to be utilized by European
immigrants. He described it as possessing desert-like characteristics, and assumed it was not
fertile enough for crop production (Last 1994). Today, Palliser’s triangle is the bread basket of
Canada. At the beginning of the twenty-first century, the glaciated planes of Canada have more
than 80% of Canada’s farmland (Boehm 2004). According to a study by the Taylor (2011), land
cover in the Northwestern Glaciated plains of the U.S. has markedly changed between 1973 and
2000. Fluctuations in precipitation determine the size of prairie potholes and lakes, and increased
moisture in the 1980s decreased the available land for crop cultivation. Also, many farmers
participated in the Conservation Reserve Program, and many crop acres were converted to
grassland (Taylor 2011).
With the introduction of European crops, other exotic plant species have also been
brought into the plains. Many species were introduced for pasture forage, and include Bromus
inermis, Agropyron cristatum, and Dactylis glomerata. Invasive species in the area that thrive in
disturbed sites include Salsola tragus, Bassia scoparia, and Melilotus officinalis (Stewart and
Kantrud 1972).
Ecoregions of Eastern Eurasia. The
Mongolian –Manchurian Steppe is
region 30. Udvardy 1975.
The Mongolian-Manchurian Steppe is part
of the Palearctic ecozone in central Asia, and covers
about 1 million square kilometers (Udvardy 1975,
McGinley 2008). The geographic range of the
steppe is bordered by Russia to the north and the
Gobi Desert to the southwest. It covers much of
Mongolia, and stretches into the northeastern region
of China, the Inner Mongolia Autonomous Region.
The topography of the areas is dominated by undulating hills and tablelands. The lands vary from
meadow steppes to desert grasslands and shrublands. The yearly average temperature within this
ecoregion ranges from -2.1 to – 3.3 ºC. Summer is the rainy season in most areas, and winters are
extremely cold and dry (Hall 1930).
This varying topography causes a wide range of climatic conditions. The Mongolian-
Manchurian ecoregion has a temperate climate (Mongolian-Manchurian grassland). The mean
elevation of the region is around 1,500 m, covering the grasslands of the Great Higgan Mountain
in the Inner Mongolia Autonomous Region to the Mongolian Plateau and desert steppe to the
west and north. The grasslands of the Great Higgan Mountains have cooler winters than
international regions with comparable latitude due to the presence of strong northwesterly winds.
The large expanse of grassland soil in the Mongolian-Manchurian Steppe is an important
part of the global carbon cycle. Mollisols in this region contains high amounts of black carbon
(BC), a product of the incomplete combustion of organic material. According to a world-wide
study of carbon in grassland ecosystems, soils of Mongolian-Manchurian Steppe contained up to
4 times more BC than similar international sites (Rodionov et al. 2010).
Biological soil crusts (BSCs) are also an important component of this rangeland system.
These crusts are comprised of intricate associations of lichens, algae, mosses, and cyanobacteria.
BSCs are critical to the stabilization and nutrient cycling of soils, especially in arid environments
(Evans. R. D. and J. R. Johansen 1993, Landgston and Neuman 2005). A study of BCSs in the
Mongolian Steppe by Liu et al. (2009) found that high density sheep grazing had a negative
impact on both BSC cover and potential nitrogen fixation compared to lower stocking rates. In
the same study, one year of grazing removal showed little regrowth of the BSC. This result was
consistent with similar studies that predict slow recovery rates of BSCs in North America, where
a Utah study of these soils that estimated historic moss cover would take up to 250 years to
reestablish (Belnap 1993). The ability of these organisms to fix nitrogen and prevent soil erosion
is critical for the growth of plants. The vegetation these soils support is important to providing
species habitat in the Mongolia-Manchurian Steppe.
Grasslands and shrublands in Mongolia and northern China are native habitat to many
plant and animal species. Drought resistant grasses such as Stipa gobica, Agropyron desertorum
as well as shrubs such as Ephedra equisetina are prevalent in the arid southwestern area of this
region, adjacent to the Gobi Desert. Other prevalent grasses include Leymus chinensis and Stipa
grandis. Shrub vegetation in the more desert-like regions include Ceratoides latens, Salsola
passerine, and Potaninia mongolica (Bai 2008). The brown-eared pheasant, Crossoptilon
mantchuricum, winters in the vegetation of these dry shrub-steppe communities. Crossoptilon
mantchuricum is the area’s only endemic bird, and the health of every constituent of the
ecosystem is necessary for the success of this species (WWF 2012). Native ungulates are also
facing challenges in the steppe. The Mongolian gazelle, Procarpa gutturosa, has been negatively
affected by the development of these rangelands. In a study of these migratory animals (Olsen et.
al. 2009), the recent erection of fences, especially on the Russian-Mongolian border have
restricted the movement of the gazelle as the ecoregion has become increasingly arid. Fences
also cause mortality to the animals. Many of these fatalities are a result of fences around trans-
rangeland railways (Olsen et. al. 2009).
These grasslands have undergone little intensive agronomic conversion compared to
many temperate rangelands world-wide due to a long history of grazing and nomadic culture
(Henwood 1998). The fertile grassland soils of the region have supported crops such as wheat
and soybeans. The Manchurian Plain has been referred to as the “Grain basket of Asia,” due to
its grain production (Hall 1930). However, sheep and goat herding has remained the major
agricultural practice in the region (Mongolian-Manchurian grassland 2012). Overgrazing has
been a result of heavy utilization, especially by goat grazing.
The Northwestern Glaciated Plains of North America and the Mongolian-Manchurian
Steppe are both important temperate grasslands. These rangelands have similar climate,
topography, and species. Both are have been impacted by drought and face the challenges of
anthropogenic utilization and development. It is important that these fragile grassland resources
continue to be studied and stewarded in order to continue providing the many ecosystem services
that are vital to the health of the planet.
References
Bai, Y., J. Wu, Q. Xing, Q. Pan, J Huang, D.Yang, and X. Han. 2008. Primary production and
the rain use efficiency across a precipitation gradient on the Mongolian Plateau. Ecology
89:2140-2153.
Belnap, J. 1993. Recovery rate of cryptobiotic crusts: inoculant use and assessment methods.
Great Basin Naturalist 53:89-95.
Boehm, M. M. 2004. The Kyoto protocol as a mechanism for improving soil quality: carbon
management on the Northern Great Plains of Canada. 13th
International Soil Conservation
Organization Conference. Conserving soil and water for society: sharing solutions.
Department of Agriculture and Agri-Food Canada, Saskatoon,
Canada.<http://www.tucson.ars.ag.gov/isco/isco13/PAPERS%20A-E/BOEHM.pdf>
Accessed 6 May 2012.
Brown, D. A. 1993. Early nineteenth-century grasslands of the Midcontinent Plains. Annals
of the Association of American Geographers 83:589-612.
Coupland, R. T. 1961 A reconsideration of grassland classification in the northern Great Plains
of North America. Journal of Ecology 49:135-167.
Evans. R. D., and J. R. Johansen. 1993. A break in the nitrogen cycle in aridlands? Evidence
from δ15
N of soils. Oecologia 94:314-317.
Hall, R. B. 1930. The Grography of Manchuria. University of Michigan. Ann Arbor, MI. <http://
deepblue.lib.umich.edu/bitstream/2027.42/67173/2/10.1177_000271623015200132.ppd>
Accessed 6 May 2012.
Henwood, W. D. 1998. An overview of protected areas in the temperate grasslands biome. Parks
8:3-8.
Kneill, C. 1993. Seasonal flooding and primary production in northern prairie marshes.
Oecologia 95:499-505.
Krapu, G. L. 2000. Temporal flexibility of reproduction in temperament-breeding dabbling
ducks. The Auk 117:640-650.
Kruse, A. D. and J. L. Piehl. 1986. The impact of prescribed burning on ground-nesting birds. In:
Clambey, G. K. and R. H. Pemble, eds. The prairie: past, present, and future. Proceedings, 9th
North American prairie conference.1984 July 29-August 1; Moorhead, MN. Fargo, ND. Tri-
College University Center for Environmental Studies 153-156.
Langston, G. and C. M. Neuman. 2005. An experimental study on the susceptibility of crusted
surfaces to wind erosion: a comparison of the strength properties of biotic and salt crusts.
Geomorphology 72:40-53.
Last, W. M. 1994. Paleohydrology of playas in the northern Great Plains: perspectives from
Palliser’s Triangle. In: Rosen, M.R. (Ed.) Paleoclimate and Basin Evolution of Playa system,
Boulder, CO. Geological Society of America Special Paper.
Liu, H., X. Han, L. Li, J. Huang, H. Liu, and X. Li. 2009. Grazing density effects on cover,
species composition, and nitrogen fixation of biological soil crust in an Inner Mongolia
Steppe. Rangeland Ecology and Management 62:321-327.
McGinley, M. 2008. World Wildlife Fund [WWF]. Mongolian-Manchurian grassland. In:
Encyclopedia of Earth. Eds. Cutler J. Cleveland.Washington, D.C. Environmental
Information Coalition, National Council for Science and the Environment.<http://www.
eoearth.org/article/Mongolian-Manchurian_grassland> Accessed 29 April 2012.
McNab, W.H. and P. E. Avers United States Forest Service [USFS] 1994. Ecological subregions
of the United States. <http://www.fs.fed.us/land/pubs/ecoregions/ ch41.html#331D>
Accessed 30 April 2012.
Mongolian-Manchurian grassland. 2012 Rivers without boundaries, Save Dauria Rivers!
<http://www.dauriarivers.org/dauria/ecosystems/grassland/> Accessed 29 April 2012.
Nesser, J. A., G. L. Ford, L. C. Maynard, and D. Dumroese. 1997. Ecological units of the
Northern Region: Subsections. Gen. Tech. INT-GTR-369. Ogden, UT: U.S. Department of
Agriculture, Forest Service, Intermountain Research Station. 88 p.
Olsen, K. A, T. Mueller, P. Leimgruber, C. Nicolson, T. K. Fuller, S. Bolortsetseg, A. E. Fine, B.
Lhagvasuren, and W. F. Fagan. 2009. Fences impede long-distance Mongolian gazelle
(Procapra gutturosa) movements in drought-stricken landscapes. Mongolian Journal of
Biological Sciences 7:45-50.
Rodionov, A., W. Amelung, N. Peinemann, L. Haumaier, X. Zhang, M. Kleber, B. Glaser, I.
Urusevskaya, and W. Zech. 2010. Black carbon in grassland ecosystems of the world. Global
Biogeochem. Cycles 24, GB3013, doi: 10.1029/2009GB003669.
Stewart, R. E. and H. A. Kantrud. 1972. Vegetation of prairie potholes, North Dakota, in relation
to quality of water and other environmental factors. U.S. Geol. Surv. Prof. Pap.
<http://library.ndsu.edu/exhibits/text/potholes/585d.html> Assessed 2 May 2012.
Taylor, J. 2011. United States Geological Survey [USGS]. Northwester Glaciated Plains
Ecoregion Summary. <http://landcovertrends.usgs.gov/gp/eco42Report.html> Accessed 29
April 2012.
Udvardy, M. D. F. 1975. A classification of the biogeographical provinces of the world. Internet
Union for Conserv. of Nature and Natural Resources. Occasional Paper No. 18. 48p.
International Union for Conservation of Nature and Natural Resources. Morges, Switzerland,
1975.United States Environmental Protection Agency [EPA] 2012. Level III and IV
ecoregions of the Continental United States.<http://www.epa.gov/wed/pages/ecoregions/
level_iii_iv.htm> Accessed 30 April 2012.
United States Forest Service [USFS] 2011.Rocky Mountain Research Station Forestry Sciences
Lab. SoLo: Ecological subsections.<http://forest.moscowfsl.wsu.edu/smp/solo/GeoPath/
subsection/S_331.php#anchor87937> Accessed 30 April 2012.
Vance, R. E. 1997. The Geological Survey of Canada’s Palliser Triangle Global Change Project:
a multidisciplinary geolimnological approach to predicting potential global change impacts
on the Northern Great Plains. Journal of Paleolimnology 17:3-8.
Van der Kamp, G. and M. Hayashi. 2009. Groundwater-wetland ecosystem interaction in the
semiarid glaciated plains of North America. Hydrogeology Journal 17:203-214.
Van der Kamp, G. and M. Hayashi. 1998. The groundwater recharge function of small wetlands
in the semi-arid northern prairies. Great Plains Research 8:39-56.
World Wildlife Fund [WWF] 2012. Ocean of grass: a conservation assessment for the northern
Great Plains. Chapter 2: The northern Great Plain ecoregion and its biodiversity context.
<http://www.worldwildlife.org/what/wherewework/ngp/
WWFBinaryitem2746.pdf > Accessed 01 May 2012.
Yansa, C. H. 1998. Holocene paleovegetation and paleohydrology of a prairie pothole in
southern Saskatchewan, Canada. Journal of Paleolimnology 19:429-441.