South African
Avocado Growers’ Association Yearbook 1987. 10:49-51.
Citrus and Subtropical Fruit Research
Institute,
Private Bag X11208, Nelspruit 1200, RSA
SYNOPSIS
Liming materials and gypsum were shown to increase avocado fruit
production when applied annually in moderate amounts, but was detrimental when
excessive applications were made. Extractable Al was shown to be a better
indicator of lime requirement than soil pH. Positive residual effects were
obtained with all treatments to a certain extent. Calcium concentrations in
both leaves and fruit were only slightly affected by these treatments, and did
not correspond with the effects obtained on yield.
Avocados are mainly grown in high rainfall areas on relatively heavy
soils in the Transvaal. Acidification is a serious problem in most orchards and
the consequences not always appreciated by growers.
Beneficial effects due to liming have been claimed by several
researchers. According to Snyman & Darvas (1982), root rot on young trees
was reduced by liming. Broadbent & Baker (1974) claimed that Phytophthora
cinnamomi did not occur on soils with a Ca status of 2 000 mg kg-1.
Koen & Smart (1973) showed that optimal growth and root development for
Duke seedlings were obtained at a soil pH (water) of 6,0 to 7,0. Fouché (1981)
stated that optimum production occurred in the pH range of 5,8 to 6,5. He also
claimed that imbalances of K, Ca and Mg in the soil will enhance pulpspot.
Kotzé & Joubert (1978) claimed that calcium silicate was not as efficient
as agricultural lime in alleviating soil acidity, and that slaked lime moved
more readily in the soil than both calcitic and dolomitic lime.
The purpose of this investigation was to compare the effect of different
calcium sources on the production of mature avocado trees grown on a fairly
acid soil, and to evaluate these sources in terms of their effects on soil acidity
and nutritional value.
Mature trees, cultivar Edrariol on Guatemalan seedling rootstock, grown
on a red clayey soil (Hutton form, Farningham series) in the Burgershall area
were used for this investigation. The treatments were as follows: four calcium
sources viz dolomitic lime, calcium hydroxide, gypsum and calcium silicate,
with three levels of each were compared with each other, as well as with a
control (no application). The levels were comparable on either neutralisation value
or calcium content. The treatments were applied annually from July 1979 to July
1982. The experiment therefore consisted of four calcium sources with three
levels each and a control, replicated four times. Plots consisted of three
trees each. The treatments are shown in Table 1. The trees were irrigated with
dragline sprinklers, with a cycle length of 10 days. No visible symptoms of Phytophthora
occurred during the period of investigation.
The trees were fertilised annually according to leaf analysis, to
maintain an optimum nutritional status. Yield data were taken annually from
1982 to 1984 as well as soil, leaf and fruit samples for analysis.
TABLE 1 Calcium sources and levels applied (ton ha-1 year-1). |
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Ca source |
Ca content (%) |
Levels* |
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|
1 |
2 |
3 |
||
|
Dolomitic lime |
37 |
2,4 |
4,7 |
7,1 |
|
Ca silicate |
34 |
2,5 |
5,0 |
7,5 |
|
Gypsum |
19 |
4,5 |
9,2 |
13,7 |
|
Ca hydroxide |
46 |
1,9 |
3,7 |
5,5 |
|
*Levels
comparable in either Ca status or neutralising ability. |
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In Table 2 the effect of three levels of each of the calcium sources is
compared mutually and with the control (no Ca treatment). The final
applications were made in 1982; therefore the 1983 data indicate the immediate
results of the applications, and 1984 the residual effects.
From the data in Table 2 it is obvious that the highest yields for 1983
were obtained with the middle levels of dolomitic lime, Ca silicate and gypsum.
The hydroxide was not significantly better than the control. It is also
noteworthy that a decrease in yield occurred with the highest levels of all
treatments. The control plot showed a drastic decrease in yield from 64 kg tree-1
in 1982 to 16 kg tree-1 in 1984.
The residual effect of calcium hydroxide and gypsum were relatively
poor, whereas good residual effects were obtained with the highest level of
calcium silicate and the middle level of dolomitic lime. The second level of Ca
silicate had a very poor residual effect, despite the fact that this was one of
the best treatments in both 1982 and 1983. The reason is unknown, although it
could be due to alternate bearing after two heavy crops.
In order to explain these differences, soil, leaf and fruit analyses
were done.
|
TABLE 2 The effect of three
levels of four different calcium sources on avocado yield(kg tree-'). |
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|
Treatment |
Level
|
1982 |
1983 |
1984 |
|
Control |
0 |
63,8 d* |
44,3 c* |
15,7 c* |
|
|
1 |
70,9 cd |
67,8 c |
56,1 ab |
|
Dolomitic lime |
2 |
125,2 a |
141,4 a |
84,1 a |
|
|
3 |
74,4 cd |
49,6 c |
50,2 ab |
|
|
1 |
92,2 be |
94,1 b |
45,0 b |
|
Ca silicate |
2 |
102,1 ab |
138,2 a |
39,3 b |
|
|
3 |
90,7 bcd |
73,0 bc |
85,2 a |
|
|
1 |
83,2 bcd |
60,7 c |
36,8 b |
|
Ca hydroxide |
2 |
81,7 bcd |
62,7 c |
45,3 b |
|
|
3 |
63,6 d |
53,8 c |
47,2 ab |
|
|
1 |
69,7 cd |
65,7 c |
33,2 b |
|
Gypsum |
2 |
103,3 ab |
102,8 b |
38,4 b |
|
|
3 |
102,6 ab |
57,5 c |
47,7 ab |
|
LSD P = 0,05 |
|
27,7 |
31,7 |
37,6 |
|
LSD P = 0,01 |
|
36,4 |
41,7 |
--- |
|
CV (%) |
|
23,1 |
29,4 |
56,5 |
|
*Values within columns with different letters differ at P=0,05. |
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Table 3 shows the initial soil composition at the start of the
experiment. It is obvious that the soil pH was very low for avocado production
(Fouché, 1981), with a very high extractable Al content of 90 mg kg-1
in the topsoil and 135 mg kg-1 in the subsoil.
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TABLE 3 Soil composition before commencement of the experiment |
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|
Factor
|
Topsoil 0-300 mm |
Subsoil 300-600 mm |
|
pH (water) |
4,8 |
4,6 |
|
|
|
|
Exchangeable cations |
|
|
|
K (mg kg-1) |
140 |
65 |
|
Ca (mg kg-1) |
130 |
90 |
|
Mg (mg kg-1) |
60 |
30 |
|
Resin P (mg kg-1) |
7 |
6 |
|
|
|
|
|
Extractable Al (mg kg-1) |
90 |
135 |
|
|
|
|
|
Texture (%) |
|
|
|
Coarse sand |
27,5 |
27,0 |
|
Fine sand |
24,5 |
23,3 |
|
Silt |
13,8 |
11,4 |
|
Clay |
34,2 |
38,3 |
In Table 4 the soil composition for 1983 is shown. These data indicate
the final treatment effects after four years of applications (1979 to 1982), as
well as the condition of the control plot. The control showed very little
difference from the original analysis, indicated in Table 3.
TABLE 4 Effect of three levels of four different
treatments on chemical composition of the top (0-300 mm) and subsoil (300-600
mm) (1983 data).
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Treatment
|
Level
|
pH (water) |
Al (mg kg-1) |
Ca (mg kg-1) |
Mg (mg kg-1) |
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|
Top |
Sub |
Top |
Sub |
Top |
Sub |
Top |
Sub |
||
|
Control |
0 |
516 |
4,63 |
93 |
158 |
194 |
38 |
59 |
20 |
|
Dolomitic |
1 |
5,40 |
5,03 |
59 |
127 |
213 |
75 |
84 |
40 |
|
lime |
2 |
5,86 |
5,31 |
34 |
103 |
288 |
100 |
125 |
47 |
|
|
3 |
5,60 |
4,81 |
65 |
115 |
206 |
69 |
92 |
35 |
|
Calcium |
1 |
5,54 |
4,79 |
79 |
89 |
275 |
88 |
35 |
18 |
|
silicate |
2 |
5,71 |
5,04 |
57 |
101 |
438 |
00 |
58 |
25 |
|
|
3 |
6,15 |
5,13 |
23 |
137 |
544 |
106 |
54 |
19 |
|
Calcium |
1 |
5,29 |
4,63 |
80 |
142 |
231 |
50 |
36 |
20 |
|
hydroxide |
2 |
5,38 |
4,84 |
68 |
43 |
331 |
100 |
32 |
18 |
|
|
3 |
5,61 |
5,30 |
69 |
90 |
475 |
213 |
29 |
20 |
|
Gypsum |
1 |
4,70 |
4,59 |
130 |
152 |
250 |
181 |
31 |
23 |
|
|
2 |
4,70 |
4,65 |
123 |
123 |
281 |
269 |
25 |
22 |
|
|
3 |
4,74 |
4,59 |
122 |
131 |
300 |
250 |
21 |
19 |
LSD P = 0,05
|
0,40 |
0,41 |
50 |
|
160 |
69 |
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