![]()
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
This research was undertaken to assess the tolerance of native and culturally significant plant species to salinity, sodicity, and flooding associated with management and disposal of CBM product water. A list of thirty-one plant species was acquired from the Environmental Protection Agency and the Northern Cheyenne Tribe. Tolerances to salinity, sodicity, flooding, and pH of plants on this list have been thoroughly researched to predict how they would respond to saline-sodic water produced from CBM development.
Table 3 provides a summary of sensitivity ratings of the thirty-one plant species found within the Northern Cheyenne Reservation to soil solution salinity (ECe), exchangeable sodium percentage, flooding, and changes in soil pH. The following explanations (a through d) have been provided to help the reader understand Table 3.
Scientific references have categorized most plants by degree of sensitivity or tolerance to salinity. Table 1 explains the general rating of plant salinity tolerances used in this report. The ECe, which measures the salinity of the soil water that is available to plants, was used to rate the salinity.
ECe |
Salinity Tolerance Rating |
Abbreviation |
< 2 dS/m |
Sensitive |
S |
2-4 dS/m |
Moderately Sensitive |
MS |
4-6 dS/m |
Moderately Tolerant |
MT |
> 6 dS/m |
Tolerant |
T |
Sodicity is expressed as SAR (sodium adsorption ratio), ESP (exchangeable sodium percentage), or as the specific sodium concentration. The rating scheme used for plant tolerances to sodium is listed in Table 2.
Sodium Tolerance Rating |
Abbreviation |
Extremely sensitive |
ES |
Very tolerant |
VT |
Data not available to justify a rating. |
No data available |
d) pH/Alkalinity Tolerance Ratings
The ideal pH ranges are given. While plant species may be able to survive outside of the given ranges, they are likely to be negatively impacted, either through direct physical damage or through competition with species better adapted to the given pH.
| Table 3. Summary of sensitivity ratings of thirty-one native and culturally significant plant species of the Northern Cheyenne Reservation to soil solution salinity (ECe), exchangeable sodium percentage, flooding, and changes in soil pH. | ||||||
Common Name |
Scientific Name |
SALINITY Rating |
SALINITY Acceptable Upper Limit ECe (sat) dS/m |
SODIUM Tolerance Rating |
Flooding Rating Limits, Inundation |
pH range |
| 1. June Service Berry | Amelanchier alnifolia | S | 2.0 | ES; ESP 2-10, SAR 1.6-8.0 | MT short term, 2 weeks | no data |
| 2. Red Osier Dogwood | Cornus stolinifera | S | 2.0 | no data available | MT short term, 2 weeks | 6.5-7.9 |
| 3. Common spikerush | Eleocharis palustris | MS | 4.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 4. Horsetail, Field | Equisetum arvense | MS | 4.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.2 |
| 5. Wild licorice/American | Glycyrrhiza lepidota | MT | 6.0 | VT; ESP 60, SAR 48 | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.2 |
| 6. Goose Berry, red shoot | Ribes setosum | S | 2.0 | ES; ESP 2-10, SAR 1.6-8.0 | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 7. Mint/Field | Mentha arvensis | S/MS | 2.0 | ES; ESP 2-10, SAR 1.6-8.0 | no data available | 4.8-7.9 |
| 8. Horsemint/W. Bergamot | Monarda fistulosa | MS | 4.0 | no data available | no data available | 5.5-7.9 |
| 9. Water Plant/Water Cress | Nasturium officinale | MS | 4.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.2 |
| 10. Sweet Medicine | Oxtropis lamnbertii | MS | 4.0 | no data available | no data available | 5.5-7.9 |
| 11. Chokecherry | Prunus virginiana | S | 2.0 | ES; ESP 2-10, SAR 1.6-8.0 | I very short term; < 2 weeks | 4.8-7.9 |
| 12. Cottonwood, G. Plains | Populus deltoides | MS | 4.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 13. Box Elder | Acer negundo | MT | 6.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 14. Green ash | Fraxinus pennsylvania | MT | 6.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 6.5-7.9 |
| 15. Sand bar willow | Salix exigua | MS | 4.0 | no data available | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 16. Snow Berry | Symphoricarpos occidentalis | MS | 4.0 | ES; ESP 2-10, SAR 1.6-1.8 | T long term, 1 year -; not tolerant of permanent flooding | 4.8-7.9 |
| 17. Cattail | Typha latifolia | MS | 4.0 | no data available | T long term, 1 year +; not tolerant of permanent flooding | 4.8-7.9 |
| 18. Wild Plum | Prunus americana | S | 2.0 | ES; ESP 2-10, SAR 1.6-1.8 | T long term, 1 year +; not tolerant of permanent flooding | no data |
| 19. Sweet grass | Hierochloe odorata | MS | 4.0 | no data available | no data available | 4.8-7.2 |
| 20. Quaking aspen | Populus tremuloides | S | 2.0 | no data available | T long term, 1 year +; not tolerant of permanent flooding | no data |
| 21. Saw beak sedge | Carex stipata | MS | 4.0 | no data available | T long term, 1 year | 5.0-7.9 |
| 22. Leafy aster | Aster foliactus | S | 2.0 | no data available | T long term, 1 year +; not tolerant of permanent flooding | 4.8-7.2 |
| 23. Stinging nettle | Urtica dioica | MS | 2.0 | no data available | I very short term, < 2 weeks | 4.8-7.2 |
| 24. Bulrush | Scirpus nevadensis | MT/T | 6.0 | no data available | T long term, 1 year +; not tolerant to permanent flooding | 4.8-7.9 |
| 25. Arrow leaf | Sagittaria latifolia | MS | 4.0 | no data available | T long term, 1 year +; not tolerant of permanent flooding | 4.8-7.9 |
| 26. Golden currant | Ribes aureum | MS | 4.0 | ES; ESP 2-10, SAR 1.6-8.0 | no available data | 4.8-7.9 |
| 27. Skunkbush sumae | Rhus trixobata | MT | 6.0 | no data available | MT short term, 2 weeks | 6.5-7.9 |
| 28. Milkweed, showy | Asclepias speciosa | MS | 4.0 | no data available | I very short term, < 2 weeks | 4.8-7.2 |
| 29. Western yarrow | Achillea millelolium | MS | 4.0 | no data available | I very short term, < 2 weeks | 4.8-7.9 |
| 30. Raspberry red | Rubes idaue | S | 2.0 | ES; ESP 2-10, SAR 1.6-8.0 | no data available | 4.8-7.9 |
| 31. Rose Bush | Rosa arkansa | MS | 4.0 | no data available | MT short term, 2 weeks | 4.8-7.9 |
a) Salinity
Generally, the most likely effect of salinity on plants is stunted growth. Increased salinity requires plants to use more energy to get water from the soil, which leaves the plant with less energy available for growth. Moderately salt-stressed plants usually appear normal, although their leaves may be darker green, thicker and more succulent than non-stressed plants. Visual symptoms (leaf burn, necrosis, and defoliation) sometimes occur, particularly in woody species. At high levels, salinity can cause physical damage and mortality. Plant sensitivity to salinity changes throughout the growing season. While most crops are relatively tolerant to salinity during germination, young developing seedlings are particularly vulnerable to salinity damage during emergence and early development. After the plants are established, they generally become increasingly tolerant of salinity in later growth stages.
One of the main effects of salinity is the delay of germination and seedling development. This delay may prove fatal if the salt-stressed seedlings encounter additional stresses, such as water stress, extreme temperature fluctuations and/or surface crusting. Also, because of evaporation at the soil surface, salt concentration in the seedbed is often higher than deeper in the soil profile. This means that roots of emerging seedlings are exposed to a greater degree of stress than indicated by usual salinity measurements which are usually averaged from soil samples taken throughout the soil profile. Plant loss during this seedling stage can reduce the plant population density to below optimal levels and significantly reduce yields.
The two main risks of high sodium levels in soil water are toxic effects and impacts on plant growth from changes in soil structure. Excess sodium present in soil water can cause soil dispersal, especially in soils with high clay contents. Soil dispersal causes loss of soil structure and surface crusting. Surface crusting leads to reduced hydraulic conductivity, reduced water infiltration, and increased water runoff. These conditions can make seedling establishment very difficult, if not impossible. Decreased drainage from sodium-induced soil dispersal can also increase the sodicity in the root zone. If water containing salts is not allowed to drain below the root zone, the salt concentration of soil water will increase as plants take up water by transpiration and as evaporation occurs. For more information on sodic soils, see "The Basics of Salinity and Sodicity Effects on Soil Physical Properties."
Sodium-induced dispersal also makes it difficult for plant roots to get the water and nutrients they need to survive. This occurs because sodic soils are likely to become and remain water logged, resulting in anaerobic conditions. If anaerobic conditions persist for more than a few days, roots fail to obtain sufficient oxygen, which reduces plant growth and can cause plant injury and eventually death.
pH is a measure of acidity or alkalinity. In general, pH less than 7 is considered acidic, pH equal to 7 is neutral, and pH greater than 7 is alkaline. The direct effect of alkalinity on plant growth is not well known. However, it is well documented that most plant species do well within a defined pH range.When abrupt changes in pH occur, plant communities shift, with more tolerant species replacing those that are less tolerant. In general, most native and culturally significant plants in arid and semi-arid environments are adapted to slightly, moderately, and strongly alkaline conditions (pH > 8).
Carbonate and bicarbonate salts are common in the waters and soils of eastern Montana, the presence of which increases soil alkalinity. Leaf burn, a known effect of bicarbonate salts on plants, occurs when bircarbonate rich water comes into contact with growing plant tissue. However, only a few very sensitive crops are negatively affected by bicarbonates. Levels high enough to affect plants are unlikely to occur under normal irrigation conditions with good drainage. Continuous flooding or frequent inundation can change these results.
1. ATTRA (Appropriate Technology Transfer for Rural Areas) Website. 2002. Agronomy Technical Note. Available at http://www.attra.org/attra-pub/bakingsoda.html
2. Ayers, R.S. and D.W. Westcot. 1976. Water Quality for Agriculture. Irrigation and Drainage Paper No. 29. Food and Agriculture Organization of the United Nations. Rome.
3. Centreconnect.org website. 2002. Available at http://www.centreconnect.org
4. Chhabra, R. 1996. Soil Salinity and Water Quality. A.A. Balkema/Rotterdam/Brookfield. New York, New York.
5. DPI (Department of Primary Industries (Queensland Government) Website. 2002. Available at http://www.dpi.qld.gov.au/fieldcrops
6.Environmental Protection Agency (EPA). 2002. Available at http://www.epa.gov
7. Interactive Biodiversity Information System website. 2002. Available at http://www.nwhi.org
8. Maas, E.V. 1993. "Testing crops for salinity tolerance." Proceeding of the Workshop on Adaptation of Plants to Soil Stresses, August 1-4,1993. University of Nebraska. Lincoln, Nebraska.
9. Miller, R. and R. Donahue. 1995. Soils in Our Environment. Simon and Schuster Company. Englewood Cliffs, New Jersey.
10. Munshower, F. 1995. Forbs, Shrubs and Trees for Revegetation of Disturbed Lands in the Northern Great Plains and Adjacent Areas. Reclamation Research Unit/ Montana State University/ College of Agriculture/ Bozeman, MT.
11. Munshower, F. 1998. Grasses and Grasslike Species for Revegetation of Disturbed Lands in the Northern Great Plains and Adjacent Areas with comments about some wetland species. Reclamation Research Unit/ Montana State University/ College of Agriculture/ Bozeman, MT.
12. National Park Service website. 2002. Available at http://www.nps.gov
13. Schafer, W.M. 1983a. Saline and sodic soils in Montana. Montana State University. MONTGUIDE 8372.
14. Schafer, W.M. 1983b. Salinity control under irrigation. Montana State University. MONTGUIDE 8382.
15. Shainberg, I., and J. Letey. 1984. "Response of soils to sodic and saline conditions. Hilgardia. 61: 1-57.
16. Shainberg, I. and J. Oster. 1978. Quality of Irrigation Water. International Irrigation Information Center. Bet Dagan, Israel
17. Small, James. 1946. pH and Plants: An Introduction for Beginners. D. Van Nostrand Company, Inc. New York, New York.
18.Tanji, K.K., Editor. 1990. Agricultural Salinity Assessment and Management. American Society of Civil Engineers. New York, New York.
19. Tisdale, S., W. Nelson, and J. Beaton. 1985. Soil Fertility and Fertilizers. Macmillan Publishing Company. New York, New York.
20. United States Department of Agriculture Website. 2002. Available at http://www.fs.fed.us/database
21. United States Geological Survey website. Available at http://biology.usgs.gov
22. Utah State University Extension Service. 2002. Available at http://extension.usu.edu
23. Watershed.org website. 2002. Available at http://www.watershed.org
24. Western Fertilizer Handbook, 8th edition. 1995. Produced by the Soil Improvement Committee of the California Fertilizer Association. Interstate Publishers, Inc., Sacramento, California, 1995.
25. Wildlife Habitat Management Institute. 2002. Available at http://www.ms.nrcs.usda.gov
26. Wild Rivers Commission website. 2002. Available at http://www.wwrc.wa.gov.au/public/waterNotes
27. Wolf, B. 1999. The Fertile Triangle. Food Products Press. Binghampton, New York.
![]() |
||
| Questions/Comments: waterquality@montana.edu |