RESPONSE OF WINTER WHEAT TO CHLORIDE FERTILIZATION IN
SANDY LOAM SOIL
K. W. Freeman1, K.
Girma1, J. Mosali2, R. K. Teal1,
K. L. Martin1 and W. R. Raun1*
1Department of
Plant and Soil Sciences, Oklahoma State University, Stillwater, OK 74078 2 The Samuel Roberts Noble Foundation, Inc., 2510 Sam Noble
Parkway, Ardmore, OK 73401
Contribution from the Oklahoma
Agricultural Experiment Station
ABSTRACT
Chloride (Cl) as a yield and
growth limiting nutrient has been the object of experimental attention for
the last several decades. Long-term experiments were conducted from 1996 to
2002 at Hennessey and Perkins, Oklahoma to evaluate the response of winter
wheat grain yield and N uptake to 0, 15 and 30 kg Cl ha-1 rates.
A randomized complete block experimental design with three replications was
used at both sites. Grain yield data were subjected to statistical analysis
using SAS. Polynomial Orthogonal contrasts were used to detect trends in
grain yield and N uptake to chloride levels. Chloride fertilizer
significantly increased wheat grain yields in 50% of the site-year
combinations (14 site years), and the increases were more notable on the
sandy loam soil included in this study.
INTRODUCTION
Chloride is an essential plant
nutrient involved in several processes taking place in the plant including
osmotic regulation (1), photosynthesis by evolution of O2 in
photosystem, enzyme activation, and transportation of other plant nutrients
(2, 3, 4), plant development, lodging prevention and disease suppression (5,
6). Chloride has also been found to control physiological leaf spotting in
some winter and durum wheat varieties and barley (7, 8).
As a yield and growth limiting
nutrient, chloride has been the object of experimental attention for the
last several decades. However recent publications related to chloride
nutrition contained contradicting reports where some reported the importance
of supplementing crops with this nutrient while others not. The latter
conclusion esteemed from the fact that chloride is required by plants in a
very small amount and this amount can be obtained from the processes in the
soil and the surrounding environments plus from fertilizers designed to
supply crops with macro-nutrients such as K and Ca (eg. KCl and CaCl2)
(9). These compounds contain some chloride in them that can be used by crops
to satisfy their requirement. Annual chloride depositions of 13 to 40 kg ha-1
in precipitation are common and may increase to more than 112 kg ha-1
in coastal areas. Due to the distance away from seawater high in Cl, inland
areas are known to receive much lower amounts of Cl in rainfall. Several of
the current chloride related research activities are focused on the benefits
obtained from chloride in suppressing foliar and root diseases (10, 11, 12,
13) than grain yield.
However, there are several
research works continued on demonstrating the importance of fertilizing
crops with chloride in USA and else where to maintain grain yields specially
in soils where the soil chloride is low such as sandy and sandy loam soils
(14). According to Grant et.al. (15) soil chloride level less than 36 kg ha-1
in the top 0.6 m of soil is generally used as an indication of insufficient
quantity and a level between 36-72 kg ha-1 is assumed to be
adequate. Chloride response to yield follows the concept of response of
crops to mobile nutrients. This means, the yield can be related directly to
the amount of chloride given this nutrient is the most limiting one in the
soil. It is also important to note that chloride is mobile and subject to
leaching. Argentina research conducted on coarse textured Mollisols showed
that, chloride fertilization increased wheat grain yields in 50% of the
sites. Averaged over 10 locations, the grain yield benefit due to chloride
fertilization was 253 kg ha -1 and it was mostly explained by a
greater number of grains per square meter (16). Soil chloride levels of
13.2 mg kg-1 were adequate for maximum grain yields (16).
Research conducted in Canada between 1996 and 1998 on clay loam and fine
sandy loam textured soils revealed that soil chloride levels were low in all
years at the fine sandy loam site and in 1996 and 1998 at the clay loam site
(17). Research in the Great Plains (showed that chloride significantly
increased wheat grain yields by as high as 1546 kg ha-1 at three
sites increasing gross return by 50 $ ha-1 (18). Generally,
wheat grown in chloride deficient soils responded positively to chloride
rates less than 50 kg ha-1. Research findings suggest that soil
(0-25 cm) chloride levels less than 33 kg ha-1, will require 22
kg Cl ha-1 applied as KCl (19). Further, the concentration of
chloride in wheat should be 0.4 percent in the whole plant at the boot to
flowering stage to achieve maximum yield potential (20). Research conducted
in the Great Plains of the USA showed that yield response occurs about half
the time when plant chloride is between 0.12 and 0.4 percent, but it occurs
80 percent of the time when plant chloride concentrations are 0.12 percent
or less (20). Similar results were also reported from research conducted in
the Pacific Northwest regions of the USA where chloride fertilization
practices increased productivity of wheat and other crops (4, 21).
One of the important functions
of chloride as a whole is its significance in suppressing some foliar
diseases. In this respect several research findings were published (10, 11,
22). All these findings documented the benefits of chloride fertilization in
lowering the negative effects of disease during the development of the crops
and the subsequent improvement in yield. In Texas, topdress applications of
chloride have caused significant reduction of leaf rust and septoria ratings
at bloom, and significant yield responses. They found a strong positive and
significant interaction between chloride and systemic foliar fungicides
which are commonly used in wheat (10).
Some researchers attribute the
chloride effect to non-disease wheat growth limiting factors (6, 23).
According to these researchers chloride fertilization is beneficial in
preventing the occurrence of a leaf spot syndrome that is not disease
related (21, 24). In support to their argument they suggested that 48 kg ha-1
chloride fertilization decreased physiological leafspot on winter wheat in
Saskatchewan.
Others claim that chloride may
increase wheat grain yields by enhancing NH4+ supply
attributed to lower leaf osmotic potentials, delayed nitrification in the
soil, and inhibition of take-all root rot (Gaeumannomyces graminis)
disease (12, 25). This is an interesting aspect of chloride since this
indicates that the uptake of major nutrients like N depends on its
availability in the soil. In fact several researchers underlined chlorides
role in uptake of other nutrients especially macro-nutrients such as
nitrogen.
In Oklahoma, research
conducted for eight years chloride on wheat grain yield and take-all disease
it was found that only in two years yield was significantly affected by
chloride levels (13). This was apparently because of the high chloride level
in the soil of the experimental site which was a silty loam. Soil survey
research across the state however, revealed that about 32% of soil samples
collected from 17 counties had chloride less than optimum for soil samples
60 cm deep (26). This means that the top soil where wheat roots are
abundant, the nutrient is below optimum level. According to this report, in
the surface soil (15 cm), 98% of the samples showed response to chloride
fertilization. Another two year and three site data in Oklahoma showed an
inconsistent response of wheat grain yield to applied chloride (27).
In
todays wheat production in Oklahoma farmers use mainly nitrogen and
phosphorus fertilizers which do not have chloride. The practice of avoiding
fertilizers containing metallic salts of chloride shows possible deficiency
of chloride in soils for crop requirement especially in high yielding deep
sandy soils with low organic matter (28). According to the National
Atmospheric Deposition Program (NADP), chloride deposition is decreasing by
0.04 kg ha-1 annually since 1983 (29) due to various measures to
reduce pollution. This indicates that chloride as a micro-nutrient needs to
be studied for cropping systems and soil conditions of a given agro-ecology.
Additionally, few studies were made to assess the effect of chloride on
uptake of N by wheat. With this in mind, long-term chloride experiments were
initiated in 1995 at two locations in different soils in Oklahoma to assess
the response of winter wheat grain yield and N uptake to chloride
fertilizer.
MATERIALS AND METHODS
Two experiments were conducted
from 1996 to 2002 at Hennessey (Shellabarger sandy loam- fine-loamy, mixed,
thermic Udic Argiustolls) and Perkins (Teller sandy loam -fine-loamy, mixed,
thermic Udic Argiustolls), Oklahoma to evaluate the response of winter wheat
grain yield and N uptake to chloride fertilizer. The Hennessey location is a
typical environment for wheat production in North Central Oklahoma. The
Perkins location is on a deep, sandy, low organic matter soil which is more
prone to leaching of mobile nutrients including chloride in soil solution.
Initial soil test data are reported in Table 1. A one to one soil to water
paste was used to extract initial soil chloride (30) and was quantified
using a Lachat (Milwaukee, WI) flow injection analyzer.
A randomized complete block
experimental design with three replications was used at both sites with
three rates of 0, 15 and 30 kg Cl ha-1 using calcium chloride
(CaCl2). Plot sizes were 4.9 m by 6.1 m.
The winter wheat variety
Tonkawa was used during the 1996 to 1999 cropping seasons. This variety
was replaced by Custer from 2000 to 2002. Wheat was planted between
October and November for all experiments at a seeding rate of 98 kg ha-1.
All other crop management practices were carried out as per the
recommendation of the respective sites. Wheat was harvested from the center
of each plot in June with a Massey Ferguson 8XP plot combine, removing an
area of 2.0 m by 6.1 m. A Harvest Master yield-monitoring computer
installed on the combine recorded yield data and sub-samples were collected.
Grain samples were dried in a forced-air oven at 66oC, ground to
pass a 140 mesh sieve (100 μm), and analyzed for total N content using a
Carlo-Erba 1500 dry combustion analyzer.
Grain yield data were
subjected to statistical analysis using SAS (31). Polynomial orthogonal
contrasts were used to detect trends in grain yield or N uptake in response
to chloride levels.
RESULTS AND DISCUSSION
Grain Yield
Chloride rates significantly
increased wheat grain yield in 50% of the year-site combinations (Tables 2
and 3). At Hennessey in 1998 a quadratic trend was observed. The response at
Hennessey in 1998 showed a common response trend of mobile nutrients such as
chloride. In 2001,
wheat grain yield increased linearly with an increase in chloride levels.
Even though not significant, an increasing linear trend in grain yield was
observed at Hennessey in 1997 as well as in 2002. In contrast, in 2000 a
decrease in yield was observed with an increase in chloride rate. The
average increment in grain yield (cf. no chloride check) averaged over years
was only 2 and 4%, respectively for 33.6 and 67.2 kg ha-1
chloride rates. The increase in grain yield for some of the years might be
attributed to nitrification inhibition in soils where pH was low as reported
by previous research (12, 32). The conditions that induce chloride response
of crops in soils such as Hennessey are primarily rainfall and pH. The
initial soil chloride levels both on the surface 0-15 cm and depth of 0-60
cm (Table 1) were slightly lower than that required for optimum yield. This
explains the irregularity in response observed at this location.
At
Perkins wheat grain yield was significantly influenced in four years in
1996, 1997, 1999 and 2000 and the average of all years. In all cases, a
linear response was observed where yield was increased with an increase in
chloride rate. Over years, 33.6 and 67.2 kg ha-1 chloride
fertilization resulted in 5.0 and 14.5% increment in grain yield. The fact
that this site is characterized by a sandy loam soil might explain the
linear response to chloride. The initial soil test level of 6.0 mg kg-1
at this site was way below the 13.2 mg kg-1 required for optimum
grain yield when chloride is the most limiting nutrient. This partially
explains why significant responses to chloride were obtained at Perkins. As
an anion, chloride is not readily adsorbed on the soil exchange complex or
organic matter and mostly present in the soil solution. Because of this,
chloride moves readily with soil water and is more prone to loss in sandy
soils. This results in a quick depletion of chloride deposited in the soil
resulting in deficiency and subsequent response of wheat to applied
chloride.
The
results from this site clearly shows that sandy loam soils in Oklahoma need
to be supplemented with chloride especially if potassium is inherently
available and if calcium is not applied to the soils since the fertilizer
form of these two nutrients contain chloride. This is an important part of
wheat management as farmers tend to supply wheat mainly with nitrogen and
phosphorus fertilizers and not potassium leading to chloride deficiency in
those soils. The results obtained here are also in agreement with previous
research reports (13, 25, 26).
Grain N
Uptake
Chloride levels affected this variable in two of seven years at Hennessey,
in one of seven years at Perkins (Table 4 and 5) and the average of years at
both locations. In 2001 at Hennessey and 2000 at Perkins a significant
linear response in grain N uptake was obtained with increasing rates of
chloride while a quadratic response was obtained at Hennessy in 1998. In
1996 and 1999 at Hennessey the N uptake decreased linearly with increasing
chloride rates even though not significant where as it was increased
linearly in 1998 and 1999 at Perkins. Although significant differences in N
uptake due to chloride fertilization were found only in three of the 14
experiments, seven experiments showed a linear increase, five of them showed
an increasing and then a decreasing quadratic response. Overall, application
of 33.6 and 67,2 kg ha-1 chloride at Hennessey site resulted in
3.5 and 5.6% grain N uptake, respectively compared with the no chloride
check. At Perkins the two chloride rates resulted in 7.5 and 14.8% increase
in grain N uptake. This suggests that chloride has a direct or indirect
effect on N uptake by wheat crop. This could be due to an antagonistic
effect of chloride on NO3- in the leaf tissue which
might have affected N uptake in grain as reported by previous research (12).
The physiological basis of this response however, needs to be further
studied.
REFERENCES
1. Kafkafi, U.; Xu, G.
Chlorine. In Encyclopedia of soil science; Lal, R., ed. Marcel Dekker:
New York, 2002; 152 155.
2.
Broyer, T.C.; Carlton, A.B.; Johnson, A.B.; Stout, P. R. Chlorine: A
micronutrient element for higher plants. Plant Physiol. 1954, 29,
526 to 532
3.
Ozanne, P.G.; Woolley, J.T.; Broyer, T.C.. Chlorine and bromine in the
nutrition of higher plants. Austr. J. Biol. Sci. 1957, 10,
66 to 79.
4. Grant, C.A.; Lamond, R.;
Mohr, R.M. Chloride research: What have we learned? 2003 ASA, CSSA, SSSA
annual meetings abstracts [CD-ROM]. ASA, CSSA, and SSSA: Madison, WI, 2003.
5. Wallace, T. The Diagnosis
of Mineral Deficiencies in Plants by Visual symptoms. Her Majesty's
Stationary Office: London, 1944; 116 pp.
6. Engel, R.E.; Ecknoff, J.;
Berg, R.K. Grain yield, kernel weight, and disease responses of winter wheat
cultivars to chloride fertilization. Agron. J. 1994, 86,
891 to 986.
7.
Smiley, R.W.; Gillespie-Sasse, L.M.; Uddin, W.; Collins, H.P.; Stoltz,
M.A.
Physiologic leaf spot of winter wheat. Plant Dis. 1993, 77,
521 to 527.
8. Engel, R. E.; Bruebaker,
L.; Emborg, T. J. A Chloride deficient leaf spot of durum wheat. Soil Sci.
Soc. Am. J. 2001, 65 (5), 1448 to 1454.
9. Carr, P.M.; Martin, G.B.;
Melchior, B.A. Spring wheat response to chloride applications in
southwestern North Dakota. Agronomy Section 2001 Annual Report Dickinson
Research and Extension Center: Dickinson, ND, 2001.
10. Miller, T.; Jungman, M.
Chloride fertilizer in winter wheat - effect of Cl and interactions with
foliar fungicides under severe leaf rust pressure. Proceedings of Intensive
Wheat Management Conference , March 4 to 5, 1998; Texas Agricultural extension
Service, The Texas A&M University System: College Station, TX, 1998.
11. Engel, R.E.; Grey, W.E.
Chloride fertilizer effects on winter wheat inoculated with Fusarium
culmorum. Agron. J. 1991, 83, 204 to 208.
12. Christensen, N.W.; Brett,
M. Chloride and liming effects on soil nitrogen form and take-all of wheat.
Agron. J. 1985, 77, 157 to 163.
13. Thomason, W.E.; Wynn, K.J.;
Freeman, K.W.; Lukina, E.V.; Mullen, R.W.; Johnson, G.V.; Westerman, R.L.;
Raun, W.R. Effect of chloride fertilizers and lime on wheat grain yield and
take-all disease. J. Plant Nutr. 2001, 24 (4&5), 683 to 692.
14.
Sillanp, M. Micronutrients and the nutrient status of the soils: A global
study. FAO: Rome, 1982.
15. Grant, C. A.; McLaren, D.L.;
Johnston, A.M. Spring wheat cultivar response to potassium chloride
fertilization. Better Crops 2001, 85 (4), 20 to 23.
16. Diaz Zorita, M; Duarte,
G. A.; Barraco, M. Effects of chloride fertilization on wheat (Triticum
aestivum L.) productivity in the sandy Pampas region, Argentina. Agron.
J. 2004, 96 (3), 839 to 844.
17. Roberts, T. L. Chloride:
Can we close the book? The Potash & Phosphate Institute (PPI) and the Potash
& Phosphate Institute of Canada (PPIC): Saskatoon, Saskatchewan Canada 1999.
18. Lamond, R.E.; Roberson,
D. D.; Rector, K. Chloride fertilization bumps wheat yields, profits. Fluid
J. 1999 Issue 27, Vol. 7, No. 4, 14 to 15.
19. Lamond, R. E.; Leikam, D.
F. Chloride in Kansas: Plant, Soil, and Fertilizer Considerations. Kansas
State University, Kansas State University Agricultural Experiment Station
and Cooperative Extension Service: Manhattan, KS, 2002; MF2570.
20. Lamond, R. How do we
manage chloride? In 2003 ASA CSSA SSSA annual meetings abstracts.
ASA CSSA SSSA, Madison, WI, 2003.
21. Engel, R.E.; Bruckner,
P.L.; Mathre, D.E.; Brumfield, S.K.Z. A chloride-deficient leaf spot
syndrome of wheat. Soil Sci. Soc. Am. J. 1997, 61, 176 184.
22. Christensen, N.W.; Taylor,
R.G.; Jackson, T.L.; Mitchell, B.L. Chloride effects on water potentials and
yield of winter wheat infected with take-all root rot. Agron. J. 1981
73, 1053 to 1058.
23. Fixen, P.E. Crop responses
to chloride. Adv. Agron. 1993, 50, 107 to 150.
24. Smiley, R.W.; Uddin,W.;
Zwer, P.K.; Wysocki, D.J.; Ball, D.A.; Chastain, T.G. Influence of crop
management practice on physiologic leaf spot of winter wheat. Plant Dis.
1993, 77, 803 to 810.
25. Koening, R.T.; Pan, W.L.
Chloride enhancement of wheat responses to ammonium nutrition. Soil Sci.
Soc. Am. J. 1996, 60, 468 to 505.
26.
Zhang, H. Soil chloride, nitrate and sulfate in Oklahoma soils. Soil
Fertility Research Highlights, Oklahoma State University: Stillwater, OK,
2000; 329 to 331.
27.
Zhang, H.; Raun, W.R. Soil chloride and sulfate status in Oklahoma soils.
Proceedings of the Southern Plant Nutrient Management Conference, October
5-6, 2004, Olive Branch, MS; Crozier, C., ed.; The Samuel Roberts Noble
Foundation: Ardmore, OK, 2004; 97 to 100.
28.
LaRuffa, J.M.; Johnson, G.V.; Phillips, S.B.; Raun,W.R. Sulfur and Chloride
Response in Oklahoma Winter Wheat. Better Crops 1999, 32 (4), 28 to 30.
29.
National Atmospheric Deposition Program (NADP). National Atmospheric
Deposition Program 2002 Annual Summary. NADP Data Report 2003. NADP
Program Office: Champaign, IL, 2003. 16 pp.
30. Diamond, D. Determination of Chloride by
Flow Injection Analysis Colorimetry. QuikChem Method 10 117 07 1 B.
Lachat Instruments: Milwaukee, WI, 1994.
31. SAS Institute. The SAS
system for windows, Version 8.02; SAS Institute: Cary, NC, 2001.
32. Roseberg, R.J.;
Christensen, N.W.; Jackson, T.L. Chloride, soil solution osmotic potential,
and soil pH effects on nitrification. Soil Sci. Soc. Am. J. 1986
50, 941 945.
Table
1. Initial soil chemical characteristics at Hennessy and Perkins sites in OK.
Samples were collected from surface (0-15 cm) except for chloride where
additional samples were analyzed from the entire 0-60 cm depth.
Location |
pH |
NH4-N
mg kg-1 |
NO3-N
mg kg-1 |
P
mg kg-1 |
K
mg kg-1 |
Cl
mg kg-1 |
Hennessey |
5.8 |
19 |
14 |
142 |
674 |
12 |
12 |
Perkins |
6.0 |
5 |
4 |
51 |
143 |
6 |
5 |
pH and Cl- 1:1 soil:water
extraction
NH4-N and NO3-N-
2 M KCl extraction
P and K- Mehlich III extraction
Soil chloride level in
the 0-60 cm depth
Table 2. Effect of chloride
fertilizer (CaCl2) on wheat grain yield at Hennessey, OK.
|
Grain Yield (Mg ha-1) |
Cl Rate
(kg ha-1) |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
Average |
0 |
2.47 |
2.07 |
4.10 |
2.31 |
4.25 |
2.20 |
3.50 |
3.00 |
33.6 |
2.40 |
2.17 |
4.50 |
2.33 |
4.23 |
2.11 |
3.89 |
3.06 |
67.2 |
2.42 |
2.66 |
4.29 |
2.10 |
4.04 |
2.44 |
3.99 |
3.13 |
SED |
0.18 |
0.50 |
0.14 |
0.20 |
0.13 |
0.10 |
0.40 |
0.09 |
Contrast |
|
|
|
|
|
|
|
|
Linear |
NS |
NS |
NS |
NS |
NS |
* |
NS |
NS |
Quadratic |
NS |
NS |
* |
NS |
NS |
NS |
NS |
NS |
NS, *, **, not significant or
significant at the 10%, 5% levels respectively.
SED-
standard error of the difference between two equally replicated means
Table 3. Effect of chloride
fertilizer (CaCl2) on wheat grain yield at Perkins, OK.
|
Grain Yield (Mg ha-1) |
Cl Rate
(kg ha-1) |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
Average |
0 |
1.16 |
0.63 |
1.62 |
0.86 |
1.21 |
2.18 |
2.78 |
1.49 |
33.6 |
1.22 |
0.66 |
1.61 |
0.89 |
1.47 |
2.16 |
2.92 |
1.56 |
67.2 |
1.47 |
0.83 |
1.92 |
1.12 |
1.67 |
2.06 |
2.87 |
1.71 |
SED |
0.12 |
0.07 |
0.19 |
0.13 |
0.16 |
0.13 |
0.14 |
0.06 |
Contrast |
|
|
|
|
|
|
|
|
Linear |
* |
** |
NS |
* |
** |
NS |
NS |
** |
Quadratic |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS, *, **, not significant or
significant at the 10%, 5% levels respectively.
SED- standard error of the
difference between two equally replicated means
Table 4. Effect of chloride
fertilizer (CaCl2) grain N uptake at Hennessey, OK.
|
Grain N uptake (kg ha-1) |
Cl Rate
(kg ha-1) |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
Average |
0 |
77.6 |
68.4 |
107.3 |
58.6 |
99.4 |
54.9 |
98.0 |
80.9 |
33.6 |
77.2 |
73.8 |
120.6 |
57.7 |
99.5 |
56.0 |
109.3 |
83.8 |
67.2 |
74.6 |
86.6 |
115.6 |
52.2 |
99.3 |
62.6 |
108.7 |
85.7 |
SED |
5.5 |
15.8 |
4.7 |
5.3 |
8.3 |
3.3 |
10.8 |
2.9 |
Contrast |
|
|
|
|
|
|
|
|
Linear |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
* |
Quadratic |
NS |
NS |
* |
NS |
NS |
** |
NS |
NS |
NS, *, **, not significant or
significant at the 10%, 5% levels respectively.
SED- standard error of the
difference between two equally replicated means
Table 5. Effect of chloride
fertilizer (CaCl2) Grain N uptake at Perkins, OK.
|
Grain N Uptake (kg ha-1) |
Cl Rate
(kg ha-1) |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
Average |
0 |
28.6 |
N/A |
29.1 |
17.8 |
21.2 |
54.4 |
66.0 |
35.7 |
33.6 |
28.2 |
N/A |
31.1 |
19.3 |
26.0 |
55.3 |
70.4 |
38.4 |
67.2 |
36.0 |
N/A |
36.8 |
21.3 |
29.8 |
52.8 |
69.2 |
41.0 |
SED |
4.5 |
N/A |
5.6 |
3.3 |
4.0 |
3.1 |
5.0 |
1.4 |
Contrast |
|
|
|
|
|
|
|
|
Linear |
NS |
N/A |
NS |
NS |
* |
NS |
NS |
*** |
Quadratic |
NS |
N/A |
NS |
NS |
NS |
NS |
NS |
NS |
NS, *, **, not significant or
significant at the 10%, 5% levels respectively.
SED- standard
error of the difference between two equally replicated means |