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African Crop Science Journal
African Crop Science Society
ISSN: 1021-9730 EISSN: 2072-6589
Vol. 8, Num. 1, 2000, pp. 63-76
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African Crop Science Journal, Vol
African Crop Science Journal, Vol. 8. No. 1, pp. 63-76, 2000
CHEMICAL COMPOSITION, PHENOLIC CONTENT AND
IN VITRO GAS PRODUCTION CONSTANTS OF FORAGE OF
PSYLLID-RESISTANT LEUCAENA SPECIES GROWN IN ZIMBABWE
L. R. Ndlovu, L. Mlambo1 and B. H.
Dzowela1
Department of Animal Science, University of Zimbabwe, P. O. Box MP167,
Harare, Zimbabwe
1Southern African Development community (SADC)- International Centre
for Agroforestry (ICRAF) Project, Department of Research and Specialist Services,
Causeway, Harare, Zimbabwe
(Received 21 September, 1998; accepted 9 Septembser, 1999)
Code Number: CS00006
ABSTRACT
Leaves from Leucaena species L. esculenta, L. diversifolia, L. pallida, L.
pulverulenta, L. salvadorensis, L. shannonii, L. trichodes and the interspecific hybrid
L. Leucocephala x L. diversifolia that are resistant to the psyllid
Heteropsylla cubana were harvested at the end of the rainy season (April) and the dry
season (November) from two sites. The leaves were either sun or oven ( 50°C) dried and
subsequently analysed for concentrations of dry matter (DM), organic matter (OM), crude
protein (CP), neutral and acid detergent fibres (NDF and ADF), lignin, extractable
proanthocyanidins (PAs), soluble phenolics (SPs) and protein precipitating potential (PPP).
In vitro gas production was measured over 72 hours. Season of harvest and method
of drying had no significant (P>0.05) effect on the variables measured. Species
significantly affected concentrations of CP, lignin, PAs, SPs and PPP. Cluster
analysis based on content of fibre or content of polyphenolics or total gas produced identified
L. shannonii, L. salvadorensis, L. esculenta and the intraspecific
hybrid L. leucocephala x L. diversifolia as potentially good quality
forages.
Key Words: Gas production, Heteropsylla cubana, leucaena, nutritive
value, phenolic, tannin
RÉSUMÉ
Les feuilles des espèces Leucaena L. esculenta, L. diversifolia, L.
pallida, L. pulverulenta, L. salvadorensis, L. shannonii, L. trichodes et les
hybrides interspécifiques L. Leucocephala x L. diversifolia qui sont
résistant aux psyllids Hétéropsylla cubana ont
été récoltées à la fin de la saison de pluies (Avril) et
à la fin de la saison de sécheresse (Novembre) à partir de deux sites.
Les feuilles ont été séchées soit au soleil ou dans un four
à (50°C) et par la suite, analysées pour les concentrations de la
matière sèche, la matière organique, les protéines brutes, les
fibres neutres et détersifs de lacide, la lignine, les proanthocyanidines extractibles,
les phénols solubles et la potentialité de précipitation des
protéines. La production de gaz (in vitro) a été
mesurée au cours de 72 heures. La saison de récolte et la méthode de
sèchement (P>0.05) navaient aucun effet impotant sur les variables
mesurés. Les espèces ont eu un effet significatif sur les concentrations de la
protéine brute, la lignine, les proanthocyanidins, les phenols solubles et la
potentialité de précipitation des protéines. Lanalyse par
groupement basée sur le contenu de fibre ou le contenu de polyphenols ou encore le
gaz total produit a identifié L. shannonii, L. salvadorensis, L.
esculenta et lhybride intraspécifique L. leucocephala x L. diversifolia
comme potentiels dêtre des fourages de bonne qualité.
Mots Clés: Production de gaz, Hétéropsylla
cubana, leucaena, valeur nutritive, phenolique, tannin
INTRODUCTION
Leucaena leucocephala is widely used as a source of high quality forage in
tropical animal production systems because of its rapid juvenile growth, high protein
concentration, high yield of digestible forage, lack of thorns and coppicing ability
(Brewbaker and Macklin, 1990). The presence of mimosine and its goitrogenic metabolite
dihydro-xypyridone (DHP) has not limited its use in systems where it is used as a supplement
(Jones, 1994). However, its value has been challenged by the outbreak of Leucaena
psyllid (Heteropsylla cubana), an aphid-like insect that produces large-scale
defoliation. Some other Leucaena species and their crosses with L.
leucocephala are resistant to psyllids (Wheeler and Brewbaker, 1990). It has been
hypothesised that the reason for the resistance to psyllid defoliation is the presence of
condensed tannins (Telek, 1992), although Wheeler et al. (1994) did not find a
significant correlation between condensed tannins and psyllid resistance.
The Southern African Development Community- International Centre for Agroforestry
(SADC-ICRAF) project has introduced several accessions of these psyllid-resistant
Leucaena species into Zimbabwe in order to assess their adaptability and potential to
supply high quality forage. The experiments described here evaluated the chemical
composition of these species, including condensed tannin concentration and in vitro
gas production. In vitro gas production provides a quick assessment and initial
screening of fodder trees (Nsahlai et al., 1994) and has been shown to be positively
related to intake (Blummel and Orskov, 1993) and microbial protein synthesis (Hillman
et al., 1993).
MATERIALS AND METHODS
Study sites. The study was conducted at two sites, Domboshava and Makoholi.
Domboshava (31°13' E, 17°30'S altitude 1530 m) has a mean annual rainfall of 895mm that
falls predominantly from November to March. Summer temperatures rise to a maximum
monthly mean of 27.9° C in October and winter temperatures fall to a minimum monthly
mean of 5.5° C in July. Evapotranspiration is highest (32 mm day-1) in
October and lowest in (14.3 mm day-1) in June (Dzowela et al.,
1995a; 1995b). The soils are ferrallisic cumbisols derived in situ from granodionite
of relatively low fertility and a predominantly sandy loam texture (Nyamapfene, 1991).
Makoholi ( 30°45'E, 19°48'S; altitude 1204 m) has a mean annual rainfall of 688 mm that
falls mainly from Nove-mber to March. The hottest month is October with a mean
temperature of 28.6°C and the lowest temperatures occur in July with a mean minimum of
6.6°C. Evapotranspiration ranges from 34.1 mm day-1 in October to 14.1 mm
day-1 in June. The soils are sandy fersiallitic with inherently low available
water holding capacity (Whingwiri et al., 1987).
The stands of the Leucaena species were defoliated by harvesting at the end of
the dry season (November) and the regrowth harvested at the end of the rainy season (April).
At each harvest, leaves were separated from stems and either sun-dried for 5 days on an open
concrete floor or oven-dried at 50°C for 48 hr. At each site there were 3 replicates for each
accession and 4 trees were harvested and bulked per replicate. In Domboshava 3 accessions
of L. diversifolia, 2 of L. esculenta, 1 of L. pallida, 1 of L.
pulverulenta, 1 of L. savadorensis, 2 of L. shannonii, 1 of L.
trichodes and 2 of an interspecific hybrid L. leucocephala X L. diversifolia ( L.l.
X L.d.) were harvested whilst in Makoholi there were 3 accessions of L. esculenta, 2
of L. diversifolia, 1 of L. pallida, 2 of L. pulverulenta, 1 of L.
shannonii and 1 of inter specific hybrid L.l. X L.d. Details of the accessions are given in
Tables 1 and 2.
TABLE 1. Chemical composition of some psyllid-resistant
Leucaena accessions grown at Domboshava
Species |
Accession number |
OM |
CP |
NDF |
ADF |
ADL |
Proanthocyanidins (A550 g-1
DM) |
Protein-precipitating potential
(mm2) |
Soluble phenolics
(g kg-1 DM) |
(g kg-1 DM) |
L. diversifolia |
OFI 35/88 |
930 |
227 |
501 |
402 |
144 |
71.9 |
90.9 |
96.3 |
OFI 45/87 |
944 |
262 |
463 |
335 |
96 |
28.8 |
55.3 |
54.6 |
0FI53/88 |
936 |
239 |
512 |
385 |
116 |
34.0 |
45.5 |
71.5 |
mean |
937 |
243 |
492 |
374 |
119 |
44.9 |
63.9 |
74.1 |
s.e. |
0.5 |
10.9 |
15.9 |
20.1 |
7.1 |
9.42 |
4.84 |
12.01 |
L.esculenta |
OFI 47/87 |
945 |
257 |
467 |
305 |
118 |
37.4 |
69.1 |
59.0 |
OFI 52/87 |
944 |
220 |
450 |
347 |
89 |
9.3 |
44.1 |
96.7 |
mean |
944 |
239 |
458 |
326 |
104 |
23.4 |
56.6 |
77.9 |
s.e. |
0.6 |
12.8 |
19.5 |
21.5 |
9.1 |
11.22 |
5.62 |
13.93 |
L. diversifolia |
ILCA 15090 |
934 |
243 |
483 |
397 |
113 |
16.6 |
49.5 |
39.5 |
ILCA 15009 |
931 |
261 |
461 |
329 |
110 |
69.7 |
54.4 |
43.1 |
mean |
933 |
252 |
472 |
363 |
111 |
43.1 |
52.0 |
41.3 |
s.e. |
0.6 |
13.6 |
19.0 |
19.0 |
9.0 |
11.22 |
5.91 |
14.29 |
L. pallida |
CPI 2137G |
943 |
218 |
446 |
423 |
126 |
25.4 |
65.3 |
45.0 |
L. pulverulenta |
OFI 83/87 |
942 |
181 |
496 |
370 |
126 |
61.6 |
120.4 |
95.8 |
L. salvadorensis |
OFI 34/88 |
930 |
271 |
455 |
314 |
71 |
8.6 |
28.8 |
37.5 |
L.shannonii |
OFI 58/88 |
928 |
231 |
543 |
361 |
99 |
2.7 |
33.8 |
46.9 |
OFI 19/84 |
938 |
214 |
520 |
365 |
79 |
2.1 |
21.1 |
28.9 |
mean |
933 |
223 |
531 |
363 |
89 |
2.4 |
27.5 |
37.9 |
s.e |
0.6 |
12.8 |
19.5 |
18.5 |
8.5 |
0.93 |
5.92 |
13.93 |
L. trichodes |
OFI 61/88 |
919 |
292 |
560 |
370 |
83 |
43.7 |
31.0 |
53.7 |
S.E. for species effect |
- |
0.7 |
15.9 |
23.7 |
31.1 |
10.7 |
14.01 |
7.40 |
17.82 |
Significance |
- |
NS |
*** |
* |
NS |
*** |
** |
*** |
NS |
OFI - Oxford Forestry Institute, CPI - Commonwealth plant identification, ILCA -
International Livestock Centre for Africa
TABLE 2. Chemical composition of some psyllid-resistant
Leucaena accessions grown at Makoholi
Species |
Accession number |
OM |
CP |
NDF |
ADF |
ADL |
Proanthocyanidins (A550 g-1
DM) |
Protein-precipitating potential
(mm2) |
Soluble phenolics
(g kg-1 DM) |
(g kg-1 DM) |
L. diversifolia |
OFI 45/87 |
898 |
312 |
560 |
392 |
103 |
35.2 |
64.5 |
117.4 |
|
0FI 53/88 |
900 |
286 |
598 |
454 |
123 |
22.4 |
49.7 |
94.7 |
|
mean |
899 |
299 |
579 |
423 |
113 |
28.8 |
57.1 |
106.1 |
|
s.e. |
10.3 |
8.6 |
18.1 |
30.9 |
14.2 |
4.21 |
3.73 |
8.75 |
L.esculenta |
OFI 47/87 |
918 |
283 |
599 |
433 |
140 |
21.4 |
48.8 |
81.6 |
|
OFI 48/87 |
902 |
247 |
552 |
387 |
141 |
31.6 |
68.8 |
126.4 |
|
OFI 52/87 |
929 |
276 |
514 |
386 |
100 |
16.2 |
47.6 |
82.5 |
|
mean |
916 |
278 |
552 |
402 |
127 |
23.0 |
55.1 |
96.8 |
|
s.e. |
9.0 |
7.3 |
15.9 |
15.4 |
11.4 |
3.76 |
3.35 |
7.56 |
L. diversifolia |
ILCA 15090 |
918 |
268 |
544 |
368 |
112 |
31.2 |
47.7 |
93.6 |
L. pallida |
CPI 2137G |
907 |
277 |
584 |
403 |
119 |
17.7 |
52.4 |
65.9 |
L. pulverulenta |
OFI 83/87 |
935 |
264 |
550 |
411 |
175 |
53.1 |
93.6 |
133.9 |
|
OFI 88/87 |
929 |
270 |
535 |
370 |
188 |
34.3 |
79.8 |
117.5 |
|
mean |
932 |
267 |
542 |
390 |
181 |
43.7 |
86.7 |
125.7 |
|
s.e |
10.3 |
8.4 |
19.4 |
29.0 |
13.2 |
4.49 |
3.98 |
9.02 |
L.shannonii |
OFI 19/84 |
910 |
329 |
566 |
383 |
112 |
8.6 |
56.0 |
77.3 |
S.E. for species effect |
|
12.1 |
9.8 |
22.0 |
25.7 |
16.1 |
5.08 |
5.74 |
10.38 |
Significance |
|
NS |
*** |
NS |
NS |
** |
*** |
*** |
** |
OFI - Oxford Forestry Institute
CPI- Commonwealth plant identification
ILCA- International Livestock Centre for Africa
Laboratory analysis. The dried samples were ground to pass through a 1 mm
screen and were analysed for concentration of dry matter (DM), organic matter (OM), crude
protein (CP) (AOAC, 1990), neutral detergent fibre (NDF), acid detergent fibre (ADF), acid
detergent fibre lignin (ADL) (Robertson and van Soest, 1981), extractable proanthocyanidins
(PAs) (Porter et al., 1986) and soluble phenolics (Reed et al., 1985). The
protein-precipitating potential (PPP) of the phenolics was estimated by the radial diffusion
method (Hagerman, 1989) and expressed as square of diameter of cleared sphere
(mm2). In vitro gas production was carried out in triplicate as
described by Nsahlai et al. (1994).
Statistical analysis. All the statistical analysis were performed using the
general linear model (GLM) procedure of SAS (1990). Data for each site were analysed
separately. The chemical analysis data were subjected to analysis of variance (ANOVA)
using a model that accounted for effects of season of harvest, drying method, species,
accession within species and two- and three-way interactions among them. None of the
interactions were significant and they were dropped from the final model.
The gas production data were fitted to the non-linear equation: Y= a + b(1-e
-ct), where Y= gas production at time t, a = gas evolved within 1 hour
and b = the volume of gas evolved with time at a fractional rate of c (Blummel and
Orskov, 1993). The gas production constants (a, b and c) were then subjected to ANOVA as
above to compare differences between accessions within species and between species.
Relationships between chemical composition, phenolic content (PAs, SPs and PPPs) and
gas production constants were established by correlations and multiple regression using a
stepwise procedure in which the variable entry criterion was set at 0.15 probability level of
significance. Cluster analysis was used to classify the accessions based on gas production
constants, fibre constituents (ADF, ADL and NDF) and phenolic content.
RESULTS
The drying method had no significant effect (P>0.05) on the concentration of
macro constituents (DM, OM, ADF, NDF, ADL, CP), phenolics and gas production constants
for either site. Season of harvest did not significantly affect concentration of phenolics and
gas production constants at either site but affected (P<0.05) the concentration of macro
constituents at Makoholi. Results on effects of species and accessions within species are
given (Tables 1 and 2).
Concentration of organic matter did not differ across species but CP varied between
species on the same site and, for some species, across sites. For example L.
shannonii had the second lowest CP at Domboshava (223 g kg-1) but the
highest at Makoholi (329 g kg-1). However, within each site the ranges of
CP concentration, though statistically significant (P<0.05), were narrow 181-292 g
kg-1 DM at Domboshava and 264-329 g kg-1 DM at
Makoholi. The content of NDF was high for L. shannonii and L. trichodes
and low for L. pallida, L. esculenta and L. pulverulenta at
Domboshava but species had no significant effect at Makoholi. The concentration of PAs
showed intraspecific variation for L. diversifolia, L. esculenta and L.l. X L.d. at
Domboshava and only for L.esculenta at Makoholi (P<0.05). For L.
esculenta, the accession Oxford Forestry Institution (OFI) 52/87 had 300 % less
concentration of PAs than accession OFI 47/87 at Domboshava but it had only 32 % more at
Makoholi. Overall, species had higher concentrations of SPs at Makoholi than at
Dombo-shava.
There were large intra-specific variations between L. esculenta and L.
pulverulenta species at Makoholi and among L. diversifolia, L. esculenta and
L.l. X L.d. at Domboshava in gas production constants (Tables 3 and 4). In general, all
species produced very little gas within 1 hour of incubation. L. shannonii produced
the highest gas volume (circa 27 ml) and L. pulverulenta had the least (circa 11 ml) at
both sites.
Correlations between chemical composition and gas production constants are shown in
Tables 5 and 6. For the Makoholi site, only PAs and DM were negatively related to total
volume of gas produced (A + B) whilst for the Domboshava site ADL, PAs, SPs and PPPs
were all negatively correlated to total volume of gas produced. Mul-tiple linear regression
equations relating chemical composition to gas production are shown in Tables 7 and 8 for
Domboshava and Makoholi, respectively. There were no significant seasonal effects
(P>0.05) for the Domboshava site but there were significant seasonal effects (P<0.05)
for the Makoholi site. PPP and PAs were poorly predicted from fibre concentration of the
browses for the Domboshava site. For the Makoholi site, PPP was poorly predicted
(R2=0.38) from fibre concentration for the herbage harvested in November
but could be better predicted (R2=0.83) from fibre concentration for the
herbage harvested in April. PAs could be predicted accurately (R2>0.9) for
both harvests from concentrations of macro constituents.
TABLE 3. Gas production constants of some
psyllid-resistant Leucaenas grown at Domboshava
Species |
Accession number |
Gas production constants |
(ml 200 mg-1) |
(ml h-1) |
a |
b |
c |
L. diversifolia |
OFI 35/88 |
0.0 |
9.1 |
0.12 |
0FI 45/88 |
0.4 |
17.5 |
0.15 |
OFI 53/88 |
0.0 |
13.6 |
0.27 |
mean |
0.2 |
13.4 |
0.02 |
s.e. |
0.07 |
0.63 |
0.003 |
L.esculenta |
OFI 47/87 |
0.6 |
20.0 |
0.01 |
OFI 52/87 |
0.5 |
16.0 |
0.01 |
mean |
0.5 |
18.0 |
0.01 |
s.e. |
0.09 |
0.82 |
0.003 |
L. diversifolia |
ILCA 15090 |
1.1 |
23.2 |
0.02 |
ILCA15090 |
0.0 |
14.4 |
0.02 |
mean |
0.5 |
18.8 |
0.02 |
s.e. |
0.08 |
0.79 |
0.003 |
L. pallida |
CPI 2137G |
0.4 |
16.7 |
0.01 |
L. salvadorensis |
OFI 34/88 |
0.9 |
25.5 |
0.06 |
L. shannonii |
OFI 58/88 |
1.0 |
25.5 |
0.03 |
OFI 19/84 |
1.0 |
27.5 |
0.03 |
mean |
1.0 |
26.5 |
0.03 |
s.e |
0.08 |
0.73 |
0.003 |
L. trichodes |
OFI 61/88 |
0.9 |
25.6 |
0.04 |
L. pulverulenta |
OFI 83/87 |
0.2 |
13.3 |
0.01 |
S.E. for species effect |
- |
0.1 |
0.96 |
0.003 |
Significance |
- |
*** |
*** |
*** |
TABLE 4. Gas production constants of some
psyllid-resistant Leucaenas grown at Makoholi
Species |
Accession number |
Gas production constants |
(ml 200 mg-1) |
(ml h-1) |
a |
b |
c |
L. diversifolia |
OFI 45/88 |
0.5 |
16.5 |
0.03 |
0FI 53/88 |
0.5 |
17.2 |
0.01 |
mean |
0.5 |
16.9 |
0.02 |
s.e. |
0.01 |
1.09 |
0.004 |
L.esculenta |
OFI 47/87 |
0.1 |
11.2 |
0.03 |
OFI 48/87 |
0.0 |
12.1 |
0.03 |
OFI 52/87 |
0.2 |
16.2 |
0.01 |
mean |
0.10 |
13.2 |
0.02 |
s.e. |
0.09 |
0.95 |
0.004 |
L. diversifolia |
ILCA 15009 |
0.5 |
17.0 |
0.02 |
L. pallida |
CPI 2137G |
0.7 |
23.1 |
0.03 |
L. pulverulenta |
OFI 83/87 |
0.1 |
11.7 |
0.01 |
OFI 88/87 |
0.0 |
11.6 |
0.03 |
mean |
0.1 |
11.6 |
0.02 |
s.e |
0.11 |
1.17 |
0.01 |
L. shannonii |
OFI 19/84 |
0.01 |
26.8 |
0.02 |
S.E. for species effect |
- |
0.13 |
1.32 |
0.004 |
Significance |
- |
*** |
*** |
NS |
TABLE 5. Correlation coefficients (P<0.05) between
chemical composition@ , phenolic content and gas production constants of
psyllid resistant Leucaenas grown in Domboshava
|
ADL |
PA |
PPP |
SP |
a |
-0.35 |
-0.47 |
-0.45 |
-0.30 |
b |
-0.43 |
-0.52 |
-0.61 |
-0.38 |
c |
-0.39 |
NS |
-0.56 |
NS |
PA |
0.32 |
* |
0.49 |
NS |
PPP |
0.40 |
0.49 |
* |
0.29 |
SP |
NS |
NS |
0.29 |
* |
@ - DM, OM, CP, NDF and ADF were not significantly correlated to
phenolic content and gas production constants
NS - Not significant P>0.05
TABLE 6. Correlation coefficients (P<0.05) between
chemical composition, phenolic content and gas production constants of psyllid resistant
Leucaenas grown in Makoholi
|
OM |
CP |
NDF |
ADF |
ADL |
PA |
PPP |
SP |
a |
NS |
NS |
NS |
NS |
NS |
-0.39 |
-0.38 |
NS |
b |
NS |
NS |
NS |
NS |
NS |
-0.39 |
NS |
NS |
c |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
PA |
0.44 |
-0.39 |
NS |
NS |
0.48 |
* |
0.61 |
0.68 |
PPP |
NS |
NS |
NS |
NS |
NS |
0.61 |
* |
0.68 |
SP |
0.63 |
NS |
NS |
NS |
0.38 |
0.66 |
0.68 |
* |
NS - Not significant P>0.05
TABLE 7. Relationships+ between
chemical composition, phenolic content and gas production of some psyllid resistant
Leucaenas harvested at Domboshava
Protein precipitating potential = 108.3 (52.15) -2.21 (1.06)NDF + 5.1
(1.56) ADL |
R2=0.36** |
Proanthocyanidins = 0.1 (0.09)ADF + 0.5 (0.17) ADL |
R2=0.32* |
Total gas = 15.1 (8.20) + 0.5 (0.16) NDF - 1.1 (0.24) ADL -0.1 (0.02)
Soluble phenolics |
R2=0.70*** |
A = 1.4 (0.24)- 0.04 (0.02)ADL - 0.004 (0.002) Soluble phenolics -0.1
(0.02) Proanthocyanidins |
R2=0.57*** |
B = 14.6 (7.61) +0.5 (0.15) NDF-1.0 (0.22)ADL-0.1 (0.002) soluble
phenolics |
R2=0.71*** |
C = 0.3(0.17) -0.003(0.0018)OM-0.007(0.0004) ADF-0.0003(0.0001)
Protein precipitating activity |
R2=0.50** |
* - P<0.05
** - P<0.01
*** - P<0.001
+ Numbers in parenthesis are standard errors of the means
TABLE 8. Relationships+ between chemical
composition, phenolic content and gas production of some psyllid resistant Leucaenas
harvested at Makoholi
November Harvest |
Protein precipitating potential = 50(56) -1.7(0.90)NDF |
R2=0.38NS |
Proanthocyanidins = 0.8(0.19)DM -0.7(0.14)NDF+0.4(0.04)ADF+
0.3(0.02)ADL |
R2=1.00** |
Total gas = No variable met the 0.15 significance level
|
- |
a = 38.8(12.28)+ 0.4(0.13)OM + 0.1(0.03)CP |
R2=0.69* |
b = No variables met the 0.15 significance level |
- |
c = 2.2(0.24) -0.003(0.001) Proanthocyanidins +0.0002(0.00008)
Soluble phenolics -0.02 (0.003) DM-0.001 (0.0003)ADL |
R2=0.97** |
April Harvest |
Protein precipitating potential = 19.1(10.21)DM -3.7(1.10)NDF +
11.2(2.61)ADL |
R2=0.83* |
Proanthocyanidins = 81.6(33.66)-0.8(0.36)DM-0.2(0.05)ADF +
0.7(0.11)ADL |
R2=0.91** |
Total gas = 22.9(3.33)-0.1(0.05)Soluble phenolics |
R2=0.51* |
a = 6.9(2.75)- 0.005(0.0025)Soluble phenolics -0.1(0.03)
OM |
R2=0.71* |
b = 22.2(3.18)-0.1(0.04) Soluble phenolics |
R2=0.50* |
c = No variable met the 0.15 significance level |
- |
* - P<0.05
** - P<0.01
NS - Not significant
Grouping of the accessions using cluster analysis suggested 3 clusters whose
membership differed with the variables used in classification (Tables 9 and 10). When fibre
constituents (ADF, ADL and NDF) were used for classification, cluster 1 contained
accessions low in ADL (circa 100 g kg-1). Cluster 2 had accessions
with medium ADL concentration (circa 120 g kg-1) and cluster 3 had
those with high ADL concentration (circa 150 g kg-1). When
clustering was based on phenolic content (PA, PPP and SP) those accessions with low PPP
(circa 46 mm2) were found in cluster 1, those with medium PPP
(circa 68 mm2) were in cluster 2 and those with high PPP
(circa 108 mm2) were in cluster 3. For gas production parameters (a,
b and c) cluster 1 had high total gas production (mean 26 ml + 1.56), cluster 2 had
medium total gas production (mean 16.2 + 2.64 ml) and cluster 3 had low gas
production (mean 11.2 + 0.53 ml).
TABLE 9. Classification of some psyllid resistant
Leucaenas from Domboshava based on fibre content, phenolics and gas production
|
Fibre content
(ADF, ADL, NDF) |
Phenolics
(PA, PPP, SP) |
Gas production
(a, b, c) |
Cluster 1 |
L. diversifolia |
OFI45/87 |
L. diversifolia |
OFI 45/87 |
L.L. X L.D |
ILCA 15090 |
L. esculenta |
OFI47/87 |
L. esculenta |
OFI 47/87 |
L. salvadorensis |
OFI 34/88 |
L. esculenta |
OFI52/87 |
L.L. X L.D |
ILCA 15090 |
L. shannonii |
OFI 58/88 |
L.L. X L.D |
ILCA 15009 |
L.L. X L.D |
ILCA 15009 |
L. shannonii |
OFI 19/84 |
L. salvadorensis |
OFI 34/88 |
L. salvadorensis |
OFI 34/88 |
L. trichodes |
OFI 61/88 |
|
|
L. pallida |
CPI 2137G |
|
|
|
|
L. shannonii |
OFI 58/88 |
|
|
|
|
L. shannonii |
OFI 19/84 |
|
|
|
|
L. trichodes |
OFI 61/88 |
|
|
Cluster 2 |
L. shannonii |
OFI 58/88 |
L. esculenta |
OFI 52/87 |
L. diversifolia |
OFI 45/87 |
L. shannonii |
OFI 19/84 |
L. diversifolia |
OFI 53/88 |
l. esculenta |
OFI 47/87 |
L. trichodes |
OFI 61/88 |
|
|
l. esculenta |
OFI 52/87 |
|
|
|
|
L. diversifolia |
OFI 53/88 |
|
|
|
|
L.L. X L.D |
ILCA15009 |
|
|
|
|
L. pallida |
CPI 2137G |
Cluster 3 |
L. diversifolia |
OFI 53/87 |
L. diversifolia |
OFI 35/88 |
L. pulverulenta |
OFI 83/87 |
L.L. X L.D |
ILCA 15090 |
L. pulverulenta |
OFI 83/87 |
L. diversifolia |
OFI 35/88 |
L. diversifolia |
OFI 35/88 |
|
|
|
|
L. pallida |
CPI 2137G |
|
|
|
|
L. pulverulenta |
OFI 83/87 |
|
|
|
|
L.L. X L. D - Leucaena leucocephala x L. diversifolia interspecific hybrid
TABLE 10. Classification of some psyllid resistant
Leucaenas from Makoholi based on fibre content, phenolics and gas production
|
Fibre content
(ADF, ADL, NDF) |
Phenolics
(PA, PPP, SP) |
Gas Production
(a, b, c) |
Cluster 1 |
L. esculenta |
OFI 52/87 |
L. esculenta |
OFI 47/87 |
L. pallida |
CPI 2137G |
|
|
L. esculenta |
OFI 52/87 |
L. shannonii |
OFI 19/84 |
|
|
L. diversifolia |
OFI 53/88 |
|
|
|
|
L.L. X L. D. |
ILCA 15009 |
|
|
|
|
L. pallida |
CPI 2137G |
|
|
|
|
L. shannonii |
OFI 19/84 |
|
|
Cluster 2 |
L. diversifolia |
OFI 45/87 |
L. diversifolia |
OFI 45/87 |
L. diversifolia |
OFI 45/87 |
L. esculenta |
OFI 47/87 |
L.esculenta |
OFI 48/87 |
L. esculenta |
OFI 52/87 |
L. diversifolia |
OFI 53/88 |
L. pulvenulenta |
OFI 84/87 |
L. diversifolia |
OFI 53/88 |
L.L. X L. D. |
ILCA 15009 |
|
|
L.L. X L.D. |
ILCA 15009 |
L. pallida |
CPI 2137G |
|
|
|
|
L. shannonii |
OFI 19/84 |
|
|
|
|
Cluster 3 |
L. esculenta |
OFI 48/87 |
L. pulverulenta |
OFI 83/87 |
L. esculenta |
OFI 47/87 |
L. pulverulenta |
OFI 83/87 |
|
|
L. esculenta |
OFI48/87 |
L. pulverulenta |
OFI 84/87 |
|
|
L. pulverulenta |
OFI 83/87 |
L.L. X L. D - Leucaena leucocephala x L. diversifolia interspecific
hybrid
DISCUSSION
Production of secondary compounds in response to herbivory and/or pathogenic
organisms is a common defense mechanism in plants (Harborne and Grayer, 1994).
Polyphenolic compounds such as tannins (proanthocyanidins and hydrolysable tannins) are a
major class of secondary compounds which are involved in these interactions (Swain, 1979).
The content of tannins in psyllid-resistant Leucaena species was thus of primary
interest in this research. These compounds bind to proteins, starch, cellulose and minerals
(Reed, 1995) thereby affecting nutrient release and supply to animals consuming forages high
in these compounds.
Current chemical assays for polyphenols do not always reflect their biological effects
(Makkar et al., 1993) and thus in this study 3 assays were used in order to encompass
as wide an array of this diverse group of compounds as possible. Biological effects were
assessed by the production of gas in vitro since tannins have been shown to interfere
with the process (Khazaal et al., 1994).
Considerable intra- and inter- specific variations in CP, ADL and polyphenolic
concentration were found. Similar results have been reported in Indian (Makkar and Singh,
1991), West African (Rittner and Reed, 1992), Greek (Khazaal et al., 1993) and
Hawaiian browse (Wheeler et al., 1994). Levels of CP were high (180-329 g
kg-1 DM) and comparable with those reported by Wheeler et al.
(1994) and Dzowela et al. (1995a) for psyllid- susceptible L.
leucocephala. At both sites, L. pallida and L. shannonii species were low
in PAs, SPs and PPP compared with L. pulverulenta. In general, however, the
browses had more SPs when grown at Makoholi than when grown at Domboshava, reflecting
a more stressful environment in the former site possibly due to lower soil fertility and
moisture levels. The SPs were determined using the ytterbium precipitation method of Reed
et al. (1985) which has been criticised as unsuitable for the determination of
total phenolics (Lowry and Sumpter, 1990). Although ytterbium does not precipitate all
phenolics, it does precipitate all phenolics with free vicinal hydroxyl groups which is a
characteristic of most tannins (Rittner and Reed, 1995). Moreover other researchers have
found that the amounts precipitated correlate well with PAs determined by both the
butanol-HCl and Vanillin-HCl method (Reed, 1995; Giner-Chavez et al., 1997).
Differences in chemical composition have a strong bearing on the nutritive value of
forages and it was hypothesised that these will be reflected in gas production parameters. The
low but significant negative correlations (0.38 - 0.6) between phenolic content and total gas
production obtained in this study (Tables 5 and 6) are indicative of the negative effect of
polyphenols on fermentation of forages. However, in multiple regression equations that
included fibre fractions, only soluble phenolics, among the tannin assays used, met the
criteria for inclusion in equations predicting total gas production (Tables 7 and 8) except for
the November harvest at Makoholi. The failure of phenolics to predict gas production in
regression equations that included fibre fractions highlights the complexity of the
interactions between fibre and polyphenols in influencing the nutritive value of forages.
There is a need for detailed analysis of chemical structural differences in polyphenolics
before these interactions can be well understood.
The gas production constants obtained in this study were lower than those reported by
Khazaal et al. (1993; 1994), Siaw et al. (1993) and Nsahlai et al.
(1994), probably due to the fact that, nitrogen (N2 ) gas instead of carbon
dioxide (CO2) was used to achieve anaerobiosis during incubations. Whilst
N2 achieved this objective, it did not lower the pH of the incubation medium
as much as CO2 would have. This could have influenced microbial activity
(Bryant, 1973) and/or complexing properties of tannins (Makkar et al., 1995).
Cluster analysis was carried out to ascertain if phenolics and gas production parameters
would group the accessions similarly. However, there was minimal overlap in the clusters
obtained from the three classification variables at both sites. This failure to obtain clusters
with largely similar membership when the classification criterion variables were chemical
components, phenolics and gas production has been reported by Siaw et al. (1993)
and Nsahlai et al. (1994) for Sesbania species. These observations therefore,
further emphasise the need to improve the understanding of the relationships between these
components as they affect nutritive value of browses.
CONCLUSION
Psyllid-resistance in Leucaena species grown in Zimbabwe was not
associated with polyphenolic concentrations substantially different from those published for
psyllid-susceptible L. leucocephala. The relationship between polyphenolic
conce-ntration and in vitro gas production constants indicated a complex interaction
with fibre concentration. At Domboshava, the interspecific hybrid L.l. X L.d. (accession
ILCA 15009) , L. shannonii species, L. salvadorensis and L. esculenta
(accession OFI 47/87) rated high in indices indicative of good nutritive value. The
corresponding accessions at Makoholi were L. shannonii OFI 19/84 and L.
esculenta OFI 52/87. These accessions require further evaluation in vivo to
determine palatability and digestibility.
ACKNOWLEDGEMENTS
The financial support of the Germany Academic Assistance programme DAAD
through a scholarship to L. Mlambo and the logistical support of the SADC-ICRAF
Agroforestry Project are gratefully acknowledged.
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©2000, African Crop Science Society
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