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224
B. A. STEWART AND C. A. ROBINSON
clear but several of the reported studies did indicate that plowing increased the decline rate. Pieri (1995) proposed that there is a critical level for soil organic matter that is dependent on the soil organic matter%age and the sum of clay plus silt.
He states that if the soil organic matter percentage falls below the critical level, the
maintenance of soil structure is difficult to achieve. However, he disagrees with
agronomists that argue that if soil organic matter is important in soil quality, then
the higher soil organic matter content is, the better the soil is. Pieri states that in
semiarid Africa, where there are so many technical and economic constraints to
crop performance, it is fruitless to aim for a soil organic matter percentage above
the critical value.
Johnson er al. (1974) reported on a 29-year study at Bushland, Texas, where various cropping systems were compared for their effects on wheat production and
soil organic matter maintenance (Table 111). They clearly showed that organic matter decline was increased when the length of the fallow period was increased or
when tillage was intensified, and the greatest loss occurred when both circumstances were present. There was also a large accumulation of nitrate nitrogen in
the soil profile for all treatments but it was particularly large for the intensively
tilled fallow areas. The delayed subtilled plots, although not socially acceptable
because of the uncontrolled weed production, had the smallest decline in soil organic matter and yielded about the same amount of wheat as the systems that controlled weed growth.
Organic matter maintenance in semiarid regions is clearly one of the greatest
constraints in the development of sustainable agroecosystems. This challenge is
particularly great in many developing countries where the crop residues are so important as a source of animal feed and fuel for cooking. Whenever feasible, it is
best to let animals graze the crop residues so the manure will be distributed over
the area. When it is necessary to utilize the crop residues as animal feed away from
the land, every attempt should be made to return manure to the land whenever feasible. Otherwise, the soil organic matter level will continue to decline to the point
that long-term sustainability of the soil resource base will be threatened. Robinson er al. (1996) reported that the maintenance or enhancement of soil organic matter is proportional to the amounts of residues returned. Maintenance of soil organic
matter is important to maintain yield potential (Bauer and Black, 1994).
MI. SUMMARY
Achieving sustainable agroecosystems is the challenge of the coming century.
With increasing population and improved living standards, the demand for food
and fiber will force the development of agroecosystems into less favorable regions.
There is often an imbalance between natural resources, population, and basic human needs in many regions and this is often particularly true for semiarid regions.
AGROECOSYSTEMS SUSTAINABLE IN SEMIARID REGIONS? 225
Agroecosystems in these areas can be developed and sustained, but careful management is required.
The prevention of soil degradation is the first and most important issue that must
be addressed in such areas. Soil degradation is a complex phenomenon. It is driven by strong interaction among socioeconomic and biophysical factors. It is fueled by increasing population, fragile economies, and poorly designed farm policies, and propelled by the fragility of the soil and harshness of the climate. Soil
degradation can be subtle and slow until a certain threshold is reached, and then
deterioration can occur quickly and, sometimes, irreversibly.
Soil organic matter is significantly correlated with soil productivity. Maintaining soil organic matter, therefore, is of critical importance. This is a tremendous
challenge in semiarid regions because insufficient precipitation seriously limits
carbon inputs and the often warm conditions accelerate the decomposition of native soil organic matter during periods of favorable soil water conditions. Extensive tillage generally increases the rate of decomposition.
There exists a considerable body of research knowledge and producer experiences. This information is sufficient in most cases to develop sustainable agroecosystems.The biggest challenge, however, is the implementation and execution
of sound management plans. Sustainable systems must focus on long-term goals,
but the reality is that short-term benefits and solutions almost always take precedence over long-term issues. Historically, agroecosystems have been developed
for short-term benefits without a thorough analysis of what long-term consequences would result. Scientists, producers, policymakers, and governments must
work together very closely in the future to meet the challenge of sustaining the natural resource base while producing adequate amounts of food and fiber.
REFERENCES
Allison, F. E. (1973). “Soil Organic Matter and Its Role in Crop Production.” Developments Soil Science. Elsevier. Amsterdam, The Netherlands.
Bauer, A,, and Black, A. L. (1994). Quantification of the effect of soil organic matter content on soil
productivity. Soil Sci. Soc. Am. J. 58, 185-193.
Brown, L. R. (1995).Nature’s limits. In “State of the World,” pp. 3-20. Norton, New York.
Brown, L. R., and Postel, S. (1987).Thresholds of change. In “State of the World,” pp. 1-19. Norton,
New York.
Cook, R. L. (1962). “Soil Management for Conservation and Production.” Wiley, New York.
Cornish, P. S., and Pratley, J. E. (1991). Tillage practices in sustainable farming systems. In “Dryland
Farming-A Systems Approach” (V. Squires and P. Tow, Eds.), pp. 76-101. Sydney Univ. Press,
South Melbourne, Australia.
Council for Agricultural Science and Technology (1988). Effective use of water in irrigated agriculture, Report No. 11 3. Council for Agricultural Science and Technology, Ames, IA.
Doorenbos, J., and Pruitt, W. 0. (1977). Crop water requirements. FA0 irrigation and drainage paper
No. 24. Food and Agriculture Organization, United Nations, Rome.
Dregne, H. E. (1989). Desertification of drylands. In “Proceedings of International Conference on Dry-
226
B. A. STEWART AND C. A. ROBINSON
land Farming, Amarillo/Bushland, Texas.” Texas Agricultural Experiment Station, College Station.
Food and Agriculture Organization, United Nations (FAO) (1978). Report on the agro-ecological zones
project. 1. Methodology and results for Africa. World Soils Resources Report No. 48. FAO, Rome.
Food and Agriculture Organization, United Nations (FAO) (1981). Agriculture: Toward 2000. Main
Report. FAO, Rome.
Francis, C., and Youngberg, G. (1990). What is sustainable agriculture? Common misconceptions about
sustainable agriculture, and historical developments relevant to the concept of sustainable agriculture. In “Sustainable Agriculture in Temperate Zones” (C. A. Francis, C. B. Flora, and L. D.
King, Eds.), pp. 3-15. Wiley, New York.
Greb, B. W. (1979). Technology and wheat yields in the Central Great Plains: Commercial advances.
J. Soil Water Consen? 34,269-273.
Greb, B. W., Smika, D. E., and Welsh, J. R. (1979). Technology and wheat yields in the Central Great
Plains: Experiment station advances. J. Soil Water Consen! 34,264268.
Halvorson, A.D. (1990). Management of dryland saline seeps. In “Agricultural Salinity Assessment
and Management” (K. K. Tanji, Ed.), ASCE Manuals and Reports on Engineering Practice No.
7 I , pp. 372-392. American Society of Civil Engineers. New York.
Hornick, S. B., and Pam, J. F. (1987). Restoring the productivity of marginal soils with organic amendments. Am. J. A/?.Agric. 2, 64-68.
Johnson, W. C., and Davis, R. G. ( I 972). Stubble-mulch farming of winter wheat: A history of 28 years’
experience at USDA Southwestern Great Plains Research Center, Bushland, Texas. USDA Agricultural Research Report No. 16. USDA, Washington, DC.
Johnson, W. C., Van Doren, C. E. and Burnett, E. (1974). Summer fallow in the southern Great Plains.
In “Summer Fallow in the Western United States,” Conservation Research Report No. 17,
pp. 86-109. Agricultural Research Service, USDA, Washington, DC.
Kanemasu, E. T., Stewart, J. I., van Donk, S. J., and Virmani, S. M. (1990). Improving productivity in
semiarid tropics. In “Dryland Agriculture: Strategies for Sustainability” (R. P. Singh, J. F. Pam,
and B. A. Stewart, Eds.), pp. 273-309. Springer-Verlag. New York.
Lal, R., and Stewart, B. A. (1990a). Soil degradation: A global threat. Adv. So;/Sci. 11. 13-17,
Lal, R., and Stewart, B. A. (1990b). Need for action: Research and development priorities. Adv. Soil
Sci. 11, 331-336.
Larson, W. E., Walsh, L. M., Stewart, B. A., and Boelter, D. H. (Eds.) (1981). “Soil and Water Resources: Research Priorities for the Nation,” pp. 229. Soil Science Society of America, Madison,
WI.
Lun, S., Zhongmin, L., Xiping, D., and Yequan, X. (1992). Field water balance under the different crop
rotations patterns in the Loess Plateau, China. In “Conservation Tillage Practices for Grain Farming in Semiarid Regions,” Proceedings International Symposium, July 7-9, (1992). Shortandy,
Kazakhstan. CIS.
Mageed, Y.A. ( 1986). “Anti-Desertification Technology and Management.” United Nations Environment Programme, Nairobi, Kenya.
Musick, J. T., and Dusek, D. A. (1971). Grain sorghum response to number, timing, and size of irrigations in the Southern High Plains. Trans. Am. SOC.Agric. Eng. 14,401404.
Musick, J. T., and Porter, K. B. (1990). Wheat. In “Irrigation of Agricultural Crops” (B. A. Stewart and
D. R. Nielsen. Eds.), pp. 598-888. American Society of Agronomy, Crop Science Society of
America, and Soil Science Society of America, Madison, WI.
Musick, 1. T., Jones, 0. R., Stewart, B. A,, and Dusek. D. A. (1994). Water-yield relationships for irrigated and dryland wheat in the U.S. Southern Plains. Agron. J. 86,980-986.
National Research Council (1993). “Soil and Water Quality: An Agenda for Agriculture.” National
Academy Press. Washington, DC.
Newcombe, K. (1984). An economic justification for rural afforestation: The case for Ethiopia. Energy Depr. Paper No. 16. World Bank, Washington, DC.
AGROECOSYSTEMS SUSTAINABLE IN SEMIARID REGIONS? 227
O’Connell. P. F. (1991). Sustainable agriculture. In “Agriculture and the Environment. The (1991 Yearbook of Agriculture,” pp. 175-185. USDA, Washington, DC.
Pierce, J. J., Larson, W. E., Dowdy, R. H., Graham, W. A. P. (1983). Productivity of soils: Assessing
long-term changes due to erosion. J. Soil Water Consen! 3 8 , 3 9 4 .
Pieri, C. (1995). Long-term soil management experiments in semiarid Francophone Africa. In “Soil
Management: Experimental Basis for Sustainability and Environmental Quality” (R. La1 and
B. A. Stewart, Eds.), pp. 225-266. CRC Press, Boca Raton, FL.
Quimby, J. R., Kramer, N. W., Stephens, J. C., Lahr, K. A., and Karper, R. E. (1958). Grain sorghum
production in Texas. Texas Agric. Exp. Stn. Bull. 912. Texas Agric. Exp. Stn., College Station.
Rangely, W. R. ( I 985). Irrigation and drainage in the world. In “Proceedings, Water and Water Policy
in World Food Supplies” (W. R. Jordan, Ed.), pp. 29-35. Texas A&M Univ., College Station.
Robinson, C. A., Cruse, R. M., and Kohler, K. A. (1994). Soil management. In “Sustainable Agriculture Systems” (1. L. Hatfield and D. L. Karlen, Eds.), pp. 109-134. Lewis, Boca Raton, FL.
Robinson, C. A,, Cruse, R. M., and Ghaffarzadeh, M. (1996). Cropping system and nitrogen effects on
mollisol organic carbon. Soil Sci. Soc. Am. J. 60, 264-269.
Rodale, R. (1988). Agricultural systems: The importance of sustainability. Phi Kappa Phi J. 2.6.
Ruttan, V. W. (1989. Spring). Sustainability is not enough. Better Crops Plant Food, 6-9.
Sharma, M. L., and Williamson, D. R. (1984). Secondary salinization of water resources in Southern
Australia. In “Salinity in Watercourses and Reservoirs” (R. H. French, Ed.), pp. 571-582. Butterworth, Boston.
Shengxiu, L., and Ling, X.(1992). Distribution and management of drylands in the People’s Republic
of China. Adv. Soil Sci.%RR 18, 148-302.
Siming, H., Chungfeng, Y., Juntong, S., and Huancheng, P. (1988). Stubble mulching in dryland on the
Loess Plateau in China. Agric. Res. Arid Areas 3, 1-12.
Souleimenov, M. K. (1992). Development of soil conservation farming practices for steppe areas of
northern Kazakhstan. In “Conservation Tillage Practices for Grain Fanning in Semiarid Regions,”
Proceeding International Symposium, July 7-9, (1992). Shortandy, Kazakhstan, CIS.
Squires, V. R. ( 199I ). A systems approach to agriculture. In “Dryland Fanning-A Systems Approach”
(V. Squires and P. Tow, Eds.), pp. 3-15. Sydney Univ. Press, South Melbourne, Australia.
Stewart, B. A. (1989). Dryland fanning: The North American experience. p. 54-59. In “Challenges in
Dryland Agriculture: AGlobal Perspective” (P. W. Unger, T. V. Sneed, W. R. Jordan, and R. Jensen,
Eds.), pp. 54-59. Proceeding International Conference Dryland Fanning, AmarillolBushland,
Texas, August 15-19, (1988). Texas Agric. Exper. Stn., College Station.
Stewart, B. A,, and Burnett, E. (1987). Water conservation technology in rainfed and dryland agriculture. In “Water and Water Policy in World Food Supplies” (W. R. Jordan, Ed.), pp. 355-359. Proceedings of the Conference, May 2 6 3 0 , (1985). Texas A&M Univ., College Station.
Stewart, B. A,, and Steiner, J. L. (1990). Water-use efficiency. Adv. SoilSci. 13, 151-173.
Stewart, B. A,, Musick, J. T., and Dusek, D. A. (1983). Yield and water-use efficiency of grain sorghum
in a limited irrigation-dryland system. Agron. J. 75,629-634.
Stewart, B. A,, Lal, R., and El-Swaify, S. A. (1991). Sustaining the resource base of an expanding world
agriculture. In “Soil Management for Sustainability” (R. La1 and F. J. Pierce. Eds.), pp. 125-144.
Soil and Water Conservation Society, Ankeny, IA.
Stewart, B. A,, Jones, 0. R., and Unger, P. W. (1993). Moisture management in semiarid temperate regions. p. 67-80. In “Agriculture and Environmental Challenges” (J. P. Srivastava and H. Alderman, Eds.), Proceedings of the 13th Agricultural Sector Symposium. The World Bank, Washington, DC.
Stewart, B. A,, Zixi, Z., and Jones, 0. R. (1994). Optimizing rainwater use. In “Stressed Ecosystems
and Sustainable Agriculture” (S. M. Virmani, J. C. Katyal, H. Eswaran, and I. P. Abrol, Eds.), pp.
253-265. Oxford & IBH, New Delhi, India.
Technical Advisory Committee (1990). “Towards a Review of CGIAR Priorities and Strategies.” Technical Advisory Committee Secretariat, Rome.
228
B. A. STEWART AND C . A. ROBINSON
Tow, P. G. and Schultz, J. E. (1991). Crop and croppasture sequences. In “Dryland Fanning-A Systems Approach” (V. Squires and P. Tow, Eds.), pp. 55-75. Sydney Univ. Press, South Melbourne,
Australia.
United Nations Educational, Scientific and Cultural Organization (UNESCO) (1977). “World Map of
Desertification,” NConf. 74/2. Food and Agricultural Organization, United Nations, Rome.
United States Department of Agriculture, Agricultural Research Service. (USDA-ARS) ( 1990).
EPIC-Erosioflroductivity Impact Calculator. Tech. Bull. 1768. USDA-ARS, Washington, DC.
Unger, P.W. (1978). Straw-mulch rate effect on soil water storage and sorghum yield. Soil Sci. Soc.
Am. J . 4 2 , 4 8 6 4 9 I .
World Bank (1986). “The World Bank Atlas.” World Bank, Washington, DC.
World Bank (1992). “World Bank Development Report.” World Bank, Washington, DC.
Zixi, Z., Stewart, B. A., and Xiandun, F. (1994). Double cropping wheat and corn in a sub-humid region of China. Field Crops Res. 36,175-183.
Index
A
Activity reports, 186
Administrators, evaluating, 188
Agricultural research, see Ethics
Agricultural themes, ethical dimensions, 155
Agriculture, sustainable, see Sustainability
Agroecosystems, 191-225
climatic effect, 201-202
increasing plant-available water, 205-223
crop calendars, 2 19-223
lengthening fallow period, 206-213
mulches, 2 13-2 I7
tillage, 217-219
productivity, 193
socioeconomic effect. 203-205
soil degradative processes, 200-201
soil effect, 202-204
soil organic matter maintenance, 223-224
stability, 194
sustainability. 194
Alfalfa. salt tolerance, 95
Animakrop mix, changing, 62
Animal feeds, promoting more efficient use of
nutrients, 62
Animal products, reducing consumption,
62-63
Animals
ethical treatment in research, 177-179
integrating into cropping system, 64
waste management, 53
Aridity index, 195
Authorship, ethics, I73
Avocado, salt tolerance, 100- I0 I
B
Bacteria, nutrient uptake stimulation, 19
Bermuda grasses, salt tolerance, 95
Berries, genetic variability and salt tolerance,
98-101
Boundaries, nutrient flows and cycles, 8-9
C
Canola, salt tolerance, 92
Carbon, decomposition dynamics, 123, 127
Chinampas, 61
Chloride, toxicity in woody species, 98-101
Citrus, salt tolerance, 100
Clover
introduction in Europe, 49
salt tolerance, 95
Commerce, ethics codes, 161
Communication, honest, with constituents,
189-190
Competition, ethics and, 179-180
Composting, low-input, on-farm, 141-144
Conflicts of interest, research ethics, 174-175
Consulting, ethics, 184
Copyright, infringement, 176
Corn
relation of yield and growing season evapotranspiration, 222
salt tolerance, 90
Costs, indirect, recovery, ethics, 171-173
Cotton, salt tolerance, 91
Cover crops, 35-36
minimizing leaching losses, 59
Credibility, establishing and maintaining, researchers, 168-169
Cropping
double, 221-222
pattern, matching with climate, 22G221
Crop residue
burning, 141
chemical composition, 122
decomposition, modeling, 125-129
expert systems and erosion models. 126
RESMAN, theory in, 126-129
as nutrient cycling, 32-33
soil protection by, 122
surface managed, decomposition, 122-125
Crops
calendars, plant-available water and, 219-223
229
230
INDEX
Crops (conrinued)
management, practices and soil ecology,
20-2 1
mix, changing, 62
rotation, 34-35
substitution as method of dealing with salinity, 76
D
Data
analysis, ethics, 167-168
collecting and reporting, ethics, 167
Decomposition
crop residue, modeling, 125-129
surface-managed crop residues, 122-125
Desertification, 204
Dust mulch. 212
E
Ecosystem relations, 9-12
Energy, use and nutrient flows, 50-52
Environmental factor, residue decomposition,
127
Environmental stresses, interactions with salinity, 84
Ethical behavior, practical principles, 152-1 54
Ethical codes, as rules, 160
Ethical disputes, resolving, 156-157
Ethics, 149-1 90
choosing research subject matter, 154157
dimensions of agricultural themes, 155
resolving ethical disputes, 156-157
science paradigm criticism, 156
sustainable agriculture, 154-155
in conduct of research, 165- I84
authorship and shared recognition, 173
collecting and reporting data, 167
competition, 179-180
conflicts of interest, 174-175
consulting, 184
data analysis, 167-168
designing experiments, 166-167
drawing and reporting inferences, 168
establishing and maintaining credibility,
168- 169
ethical treatment of animals, 177-179
indirect cost recovery, 171-173
intellectual property rights, 175-177
peer review, 173
performing to specifications, 180
proposal budgets, 17I
proposal preparation, 169-170
technology transfer, 180-183
topic selection, 166
whistle-blowing, 173-174
definitions, 151
difficultieswith utilitarian approach, 158-162
abiding by rules, 162
difficulty in evaluating outcomes, 158
ethics codes as rules, 160-162
evaluation of principles, 159-160
sea of uncertainty, 158-159
personal and group, 151-152
research administration, 184-190
activity reports, 186
equity and merit, 189
evaluating administratorsand managers,
188
hiring and termination, 184-185
honest communication with constituents,
189-1 90
job applications, 188
letters of recommendation,support, and
evaluation, 186- I87
nurturing scientists, 185-186
promotion documents and decisions, 187
scientific misconduct, 152
world food situation and, 162-165
driving forces, 162-164
message for agronomists, 165
moot questions, 164-165
sources of research support, 165
Experiments
designing, ethics, 166167
drawing and reporting inferences, 168
Expert system, residue decomposition models,
126
F
Fairness, 153, 189
Fallow period
efficiency and tillage, 218
lengthening, 206-2 13
mulch and plant-availablewater, 214-217
Fertilizers
overuse, 2-3
utilizing more efficiently, 60
23 1
INDEX
Field crops, genetic variability and salt tolerance, 9 1-92
Field screening techniques, salt tolerance, 103
Flow nutrients, nearby, agricultural use, 61
Food, consuming local produce, 64
Forages, genetic variability and salt tolerance,
94-95
Fruits, genetic variability and salt tolerance,
98-101
Fungi, nutrient uptake stimulation, 19
G
Genes, salt tolerance, 101-102
Geologic deposits, nutrient dynamics, 50
Grains, genetic variability and salt tolerance,
88-91
Grasses, genetic variability and salt tolerance,
94-95
H
Harvest, nutrient loss, 24-26
Heritability, salt tolerance, 103
Hiring, ethical, 184-185
Honesty, 152-153
Human waste, land application, 53
I
Immobilization, inorganic nutrients, 18-19
Inorganic nutrients, immobilization, 18-19
Integrity, 153
Intellectual property rights, ethics and,
175-177
Ion
accumulation, salt tolerance and, 86
selectivity, salt tolerance and, 85-86
Irrigation, increasing salinity of lands and, 76
J
Job applications. I88
K
Kentucky bluegrasses, salt tolerance, 95
L
Land, increased yield, 192
Letters of recommendation, support, and evaluation, 186-187
Lettuce, salt tolerance, 98
Linseed, salt tolerance, 93
M
Managers, evaluating, 188
Manure
nutrient flow, 40
utilizing more efficiently, 60
Melon, salt tolerance, 97-98
Merit, rewarding, equity and, 189
Military, ethics codes, 161-162
Mineralization, 14-15
soil organic matter, 18
Modeling, salt tolerance, 107
Molecular biology, salt tolerance, 106-107
Mulches, increasing plant-available water,
21 3-2 I7
N
Nitrate leaching, 26.42
Nitrogen
decomposition dynamics, 123, 127
fixation, 19
by symbiotic and nonsymbiotic organisms,
6M1
recommendations, 30-3 1
Nondisclosure agreements, 177
No-till cropping systems, 121-144
deleterious rhizobacteria for weed control,
137-141
domination by fungi and earthworms, 136
low-input, on-farm composting, 141-144
root-microbial relationships, 129-1 37
Nutrient cycle, 8
crop residues, 32-33
ecology, 17-2 1
efficiency, 9-10
plant strategies, 10
simplified managed system, 10-1 1
simplified natural system, 9-10
Nutrient dynamics, 1-66: see also Soil-plant
system
definitions, 7-9
232
INDEX
Nutrient dynamics (continued)
energy use and nutrient flows, 50-52
farm-level changes, 60-62
farm-scale cycling and Rows, 3 8 4 7
to and from farms, 4 0 4 3
between farms, 43-44
nutrient exports > imports, 44-46
nutrient exports < imports, 46
nutrient exports = imports, 46-47
within-farm, 3 9 4 0
at field level, 23-38
changes in nutrient, 36-37
changing to biologically based nutrient
sources, 37-38
cover crops, 35-36
crop residues, 32-33
crop rotation, 34-35
inadvertent nutrient losses, 26-27
nutrient additions, 27-3 1
nutrient losses, 24-27
pastures, 35
tillage systems, 33-34
field-level changes, 58-60
finite geologic deposits, 50
harvest removal, 24-26
historical overview, 5-7
increasing soil nutrient availability, 5 9 4 0
influences on flow patterns, 54-56
intercontinental flows, 49-50
landscape position, 12-13
possible changes in large-scale flows, 52-54
seasonal patterns, 12-1 3
societal-level changes, 6 2 4 5
spatial cycle and ecosystem relations, 9-12
spatial scale of changes and time needed to
complete, 57-58
utilizing fertilizers and manures more efficiently, 60
utilizing more efficiently taken up nutrient
sources, 60-6 I
watersheds, 4 7 4 8
Nutrient flow, 8
ecology, 17-2 1
field, changes in, 3 6 3 7
patterns, potential implications, 44-45
Nutrient leaks, 62-63
Nutrients
added, quantity, 29-3 I
application timing and methods, 28-29
balances, mixed crop and livestock farm, MI
degree of synchronization between availability and uptake needs, 58-59
enhancing uptake efficiency, 58-59
management issues, 2-4
sources
biologically based, 37-38
soluble, sparing use, 61
transformations, ecology, 17-2 I
transporting back to farmland, 64-65
Nuts, genetic variability and salt tolerance, 98-101
0
Oil seed crops, genetic variability and salt tolerance, 92-93
Organic matter
maintenance, semiarid regions, 223-224
semiarid regions, 21 1
Ornamentals, genetic variability and salt tolerance, 101
Osmotic adjustment, salt tolerance and, 87
P
Pastures, 35
Patent, infringement, 176
Peer review, ethics, 173
Performing to specifications, I80
Phosphorus, solubility, 19
Plant-animal-human trophic pyramid, segment
separation, 6 3 4 5
Plant nutrition, 13-17
Potato, salt tolerance, 92
Practices
advocating, 182-183
testing and comparing, 181-182
Products
advocating, 182-1 83
testing and comparing, 18 1-1 82
Promotion, documents and decisions, 187
Proposals
budgets, ethics and, 17 1
preparing, ethics and, 169-1 70
R
Research, see Ethics
RESMAN, theory used in, 126-129
Rhizobacteria, deleterious, 129-1 32
weed control, 137-141
INDEX
Rice, salt tolerance, 90-91
Root environment, optimizing, 59
Root-microbial relationships, 128-1 37
deleterious rhizobacteria, 129-132
root zone temperature and, 133
Ruminant livestock, biological nitrogen fixation,
4041
S
Safflower, salt tolerance, 92-93
Salinity problems, semiarid regions, 212
Salt, accumulation, 86
Salt stress, short- and long-term effects, 85
Salt tolerance, 75-108
breeding methods, 101-105
field screening techniques, 103
genes for tolerance, 101- 102
heritability, 103
selection methods. 104-105
crop species, 77
genetic variability, 88-101
field crops, 91-92
fruit, nuts, and berries, 98-101
grains, 88-9 I
grasses and forages, 94-95
oil seed crops. 92-93
ornamentals, 101
vegetable crops, 95-98
in low-yielding varieties, 81
measurement, 79-80
mechanisms, 84-88
ion accumulation, 86
ion selectivity,85-86
organic solutes, 87
osmotic adjustment, 87
water use efficiency. 87-88
modeling, 107
molecular biology, 106-107
rationale for breeding for, 77-78
selection for. 78-84
environmentalinteractions, 84
growth stage, 82-83
specific ion tolerance, 83-84
yield and productivity, 80-82
tissue cultures, 105-106
Science, pure, ethics codes, 161
Science paradigm. criticism, 156
Scientific misconduct, 152
Scientists, nurturing. 185-1 86
233
Seasonal patterns, nutrient dynamics, 12-13
Selection methods, salt tolerance, 104-105
Semiarid regions, 194-198
aridity index, 195
characterization, 192
example locations, 196-198
length of growing period, 195-196
soil organic matter maintenance, 223-224
Soil
chemical properties, 21
degradation, interdependenceon biological
and socioeconomicfactors, 203, 205
effect on sustainability,202-204
erosion, 26
fertility, maintaining long-term, 15-17
management, practices and soil ecology,
20-2 1
nutrients, increasing availability,5 9 4 0
nutrient stocks, 13-17
organic matter
depletion, 3
dynamics, 17
maintaining high levels, 15-16
mineralization, 18
physical properties, 2 1-22
Soil-plant system, 13-23
biological, chemical, and physical interactions, 22-23
ecology of nutrient flows, transformations,
and cycles, 17-21
maintaining long-term soil fertility, 15-1 7
satisfying short-term fertility needs, 14-15
simplified nutrient cycle, flows, and transformations, 14
Soil resources, wasteful use, 62
Solutes, organic, salt tolerance and, 87
Sorghum
relation of yield and seasonal evapotranspiration, 208
salt tolerance, 90
Soybean, salt tolerance, 92
Spacial scale, 9-12
Stocks, 7-8
Straw mulch, 215-216
Stubble mulching, 213-215
Sugar beet, salt tolerance, 91-92
Summer fallow, 206.21 1-213
Sunflower, salt tolerance, 93
Sustainability,4, 56-57, 194, 198-205
climatic effect, 201-202
2 34
INDEX
Sustainability (conrinued)
definition, 198
ethics and, 154-155
reasons for importance in policy agenda,
199
socioeconomic effect, 203-205
soil effect, 202-203
T
Technology transfer, ethical issues, 180-1 83
Technology transfer agents, responsibility,
181
,
Temperature function, residue decomposition,
128
Termination, of employees, 185
Tillage, plant-available water and, 217-219
Tillage systems, 33-34
Tissue cultures, salt tolerance, 105-106
Tomato, salt tolerance, 97
Trade secrets, ethics and, 176177
Transformations, 8
Trophic pyramid, 5
V
Vegetable crops, genetic variability and salt tolerance, 95-98
W
Water, plant-available, technologies for increasing, 205-225
crop calendars, 2 19-223
lengthening fallow period, 206-213
mulches, 2 13-2 17
tillage, 217-219
Water function, 127
Watersheds, nutrient dynamics, 47-48
Water use, efficiency and salt tolerance, 87-88
Weed control, deleterious rhizobacteria,
137-14 1
Wheat
relation of yield and growing season evapotranspiration, 222
relation of yield to seasonal evapotranspiration, 208-210
salt tolerance, 89-90, 102
Wheatgrass, salt tolerance, 94
Whistle-blowing, ethics, 173-174
Winter wheat
deleterious rhizobacteria effect, 129-132
high crown set, 141-142
rhizoplane populations of inhibitory
pseudomonads, 134-1 35
yield from fields inoculated with rhizobacteria, 138
World food, ethics and, 162-165