Crop Nutrition Changes in Zero Till Over Time
Rigas E. Karamanos
Western Cooperative Fertilizers Limited,
P.O. BOX 2500, Calgary, AB T2P 2N1
Crop Nutrition is defined as the supply and absorption of chemical compounds needed for growth and metabolism (Mengel and Kirkby 1979). Implementation of zero tillage results in a number of changes in the whole soil-plant-system that can directly or indirectly affect crop nutrition. Some of the most important changes are related to the effect of accumulation of residues directly on the soil surface and lack of soil disturbance in a zero tillage system.
Any change in crop nutrition under long-term zero tillage will be reflected in the supplying power and, hence, availability of nutrients. Therefore, this presentation looks at the impact zero tillage might have on the supplying process(s) of soil nutrients and soil properties that might affect the same. A brief conclusive statement on the findings from a variety of scientists is included in the Tables below.
Changes in crop nutrition of nitrogen in zero till over time.
|
Supply Processes |
Changes through Zero Till |
Location |
References |
|
Mineralization (Conversion of organic N to inorganic N as a result of microbial decomposition) |
No effect |
SW Saskatchewan |
Jowkin and Schoenau 1995 |
|
Reduction especially under drier conditions |
Lethbridge and Vauxhall, AB |
Carefoot et al. 1990 |
|
|
Conclusion: Nitrogen mineralization may be decreased through zero tillage |
|||
|
Mineralizable (or Labile) N (Pool of soil N that contains forms which can be converted to inorganic N by micro organisms) |
Greater mineralizable N levels |
CO, NE, SD, ND |
Doran et al. 2000 |
|
Increased after 7-8 years depending on soil texture |
Swift Current, SK |
Campbell et al. 1997 |
|
|
Increased with magnitude depending on rotation |
Seven sites in SK |
Curtin et al. 1996 |
|
|
Increased after 11 years |
Cantaur, SK |
Campbell et al. 1995 |
|
|
Increased after 16 years |
South Texas |
Salinas-Garcia et al. 1997 |
|
|
Increased after 16 years |
Sidney, NE |
Tracy et al. 1990 |
|
|
Increased after 14 years |
Melfort, SK |
Selles et al. 1984 |
|
|
Conclusion: Mineralizable nitrogen increases through zero tillage |
|||
Changes in crop nutrition of nitrogen in zero till over time (continued).
|
Supply Processes |
Changes through Zero Till |
Location |
References |
|
Immobilization (Conversion of inorganic N to organic N) |
Higher, i.e., potential for N conservation |
Ellerslie, AB |
Haugen-Kozyra et al. 1993 |
|
Higher – indirectly through higher total N levels |
Eastern Kansas |
Havlin et al. 1990 |
|
|
Conclusion: Nitrogen immobilization increases through zero tillage |
|||
|
NO3-N accumulation (Residual NO3-N) |
Lower (mechanism? Lower mineralization or higher denitrification?) |
Indian Head, SK |
Grant and Lafond 1994 |
|
No difference in a continued wheat system, but increased in a fallow-wheat system |
Cantaur, SK |
Campbell et al. 1995 |
|
|
No difference |
SW Quebec |
Burgess et al. 1999 |
|
|
Lower (attributed to lower net mineralization in zero till plots) |
Central AB |
Nyborb and Malhi 1989 |
|
|
No difference in a corn-soybean rotation |
Quebec |
Rembon and MacKenzie 1997 |
|
|
Conclusion: Generally nitrate-nitrogen or "available" nitrogen levels are not affected by tillage |
|||
|
Symbiotic Fixation (Conversion of atmospheric N to protein by heterotrophic bacteria living in association with a host legume) |
Higher (due to reduced soil nitrate found in zero tillage) |
Indian Head, SK |
Matus et al. 1996 |
|
Readily available from crop residues (Direct leaching from crop residues) |
Higher by 25% |
Growth chamber |
Roppel 1991 |
Changes in crop nutrition of sulphur in zero till over time.
|
Supply Processes |
Changes through Zero Till |
Location |
References |
|
Mineralization |
Higher at surface 2 inches |
Sidney, NE |
Tracy et al. 1990 |
|
Available -Labile |
No impact |
Indian Head, SK |
Grant and Lafond 1994 |
Changes in crop nutrition of phosphorus in zero till over time.
|
Supply Processes |
Changes through Zero Till |
Location |
References |
|
Available -Labile |
No impact |
Indian Head, SK |
Grant and Lafond 1994 |
|
No impact |
Michigan |
Daroub et al. 2000 |
|
|
No impact on organic P pool, but labile inorganic P was increased |
Ste. Anne de Bellevue, PQ |
O’Halloran 1993 |
|
|
Increased in the top 2 inches |
Lexington, KY |
Ismail et al. 1994 |
|
|
Conclusion: Generally "available" phosphorus levels are not affected by tillage |
|||
|
Mineralization |
Higher |
Sidney, NE |
Tracy et al. 1990 |
|
Readily available from crop residues (Direct leaching from crop residues) |
Higher |
Growth chamber |
Schoenau 1995 |
|
Mycorrhizae (fungi living in association with plant roots) |
Higher (however, no yield benefit due to other factors limiting early growth) |
Guelph, ON |
McGonigle and Miller 1996 |
|
Conclusion: Generally phosphorus supplying processes are enhanced under zero tillage but yield benefits are not always evident |
|||
Changes in crop nutrition of potassium in zero till over time.
|
Supply Processes |
Changes through Zero Till |
Location |
References |
|
Available -Labile |
No impact |
Indian Head, SK |
Grant and Lafond 1994 |
|
Higher |
Ft. Collins, CO |
Follett and Peterson 1988 |
|
|
Higher (due to increase in organic matter levels under 16 years of zero tillage) |
Lexington, KY |
Evangelou and Blevins 1988 |
|
|
Increased in the top 2 inches |
Lexington, KY |
Ismail et al. 1994 |
|
|
Conclusion: Generally "available" potassium levels are increased under zero tillage |
|||
Changes in soil biological/biochemical characteristics/properties in zero till over time.
|
Characteristic/Property |
Changes through Zero Till |
Location |
References |
|
Microbial biomass |
No impact |
Brandon and Minnedosa, MB |
Banerjee et al. 1999 |
|
Increased or remained the same |
Ft. Vermillion, AB |
Lupwayi et al. 1999 |
|
|
Higher than conventional tillage |
Sidney, NE |
Follett and Schimel 1989 |
|
|
Higher than conventional tillage |
CO, NE, SD, ND |
Doran et al. 2000 |
|
|
Higher than conventional tillage only after 11 years |
Swift Current, SK |
Campbell et al. 1997 |
|
|
Higher than conventional tillage |
Seven sites in SK |
Curtin et al. 1996 |
|
|
Conclusion: Generally zero tillage resulted in higher microbial biomass compared to conventional tillage |
|||
|
Enzymatic activity |
No impact (on arylsulfatase or acid and alkaline phosphatase) |
Brandon and Minnedosa, MB |
Banerjee et al. 1999 |
|
Increased (dehydrogenase, urease, glutaminase, B-glucosidase, arylsulfatase and phosphatase) |
NW Ontario |
Bergstrom and Monreal 1995 |
|
|
Increased |
760 soils |
Monreal and Bergstrom 2000 |
|
|
Conclusion: Generally zero tillage resulted in higher enzymatic activity compared to conventional tillage |
|||
|
Respiration |
Decreased |
Ft. Vermillion, AB |
Lupwayi et al. 1999 |
|
Humidified C fractions |
Increased |
S Ontario |
Yang and Kay 2001 |
Changes in soil physical characteristics/properties in zero till over time.
|
Characteristic/Property |
Changes through Zero Till |
Location |
References |
|||||
|
Aggregate stability and/or aggregate size distribution |
Increased |
Seven sites in SK |
Curtin et al. 1996 |
|||||
|
Greater |
Biggar, SK |
Ellitt and Efetha 1999 |
||||||
|
Greater |
Ohio |
Mahboubi et al. 1993 |
||||||
|
Conclusion: Generally zero tillage resulted in greater aggregate stability and/or aggregate size distribution |
||||||||
|
Water infiltration |
Greater |
Biggar, SK |
Ellitt and Efetha 1999 |
|||||
|
Greater after 20 years |
S. Alberta |
Chang and Lindwall 1989 |
||||||
|
Conclusion: Generally zero tillage resulted in greater water infiltration |
||||||||
|
Bulk density |
No difference |
Lethbridge and Vauxhall, AB |
Carefoot et al. 1990 |
|||||
|
No difference after 24 years |
S Alberta |
Miller et al. 1999 |
||||||
|
No difference after 20 yrs (but conventional tillage was very shallow) |
S. Alberta |
Chang and Lindwall 1989 |
||||||
|
Conclusion: Generally bulk density of surface horizons was not affected by tillage |
||||||||
|
Soil water content |
Increased or remained the same |
Lethbridge and Vauxhall, AB |
Carefoot et al. 1990 |
|||||
|
Increased |
Saskatoon, SK |
Moazed anf Maule 1996 |
||||||
|
Conclusion: Generally zero tillage resulted in greater soil water content |
||||||||
|
Soil pores |
Pores from 100- to 500-mm diameter increased after 4 years |
S Ontario |
VandenBygaart et al. 1999 |
|||||
|
Larger pores (30-40, 40-67, 67-200, >200 mm) higher |
S Alberta |
Miller et al. 1999 |
||||||
|
No difference after 20 yrs (but conventional tillage was very shallow, 3.5") |
S. Alberta |
Chang and Lindwall 1989 |
||||||
|
Conclusion: Generally zero tillage resulted in greater number of larger pores |
||||||||
Changes in soil physical characteristics/properties in zero till over time (continued).
|
Plant-available water-holding capacity |
Decreased |
S Alberta |
Miller et al. 1999 |
|
Increased |
Wooster and A Charleston, OH |
Mahboubi et al. 1993 |
|
|
No difference after 20 yrs (but conventional tillage was very shallow, 3.5") |
S. Alberta |
Chang and Lindwall 1989 |
Conclusions
Zero tillage was introduced primarily as a means of conserving water in arid and semi-arid areas of the world. However, implementation of zero tillage results in significant changes of many of the physical, chemical, physicochemical, biological and biochemical properties of soils. All these changes are expressed in a modification of crop nutrition, i.e., the supply and absorption of chemical compounds needed by plants for growth and metabolism. Time since implementation of zero tillage and mode of conventional tillage would largely determined the differences between the two systems and the net benefit, if any, of zero tillage. Of the major nutrients, zero tillage results in significant changes in the supply and absorption of nitrogen and potassium, whereas phosphorus and potassium seemingly remain unaffected or their contribution is superseded by other factors. Improvement in crop nutrition is also a result of improvements in soil quality that influences both supply and absorption of nutrients thus affected.
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