In the North of Vietnam the increasing use of insecticides to control insect pests in the rice fields is causing serious problems in terms of residues in rice and surface and ground water, resulting in health concerns for both humans and livestock. Two experiments were carried out therefore to investigate the effects of growing and laying ducks, either alone or together with fish, on net economic benefits for small rice farmers and on insecticide residue levels in paddy rice and water. The treatments in Experiment 1 were: Rice with and without insecticides (R), and ducklings-rice (DR) with no insecticides applied.
Rice yield was
not affected by treatment and was 4013 and 4015 kg/ha for R and
DR, respectively. The maximum residue limit (MRL) for insecticides was 4.2 g/kg
paddy for the rice only (R) treatment, which is considered potentially
dangerous. Net economic benefit for rice only was 2.72 million VND/ha, and for
ducklings-rice was 9.91 million VND/ha.
In Experiment 2 the treatments were: Rice only (R) with insecticides applied; Ducks and rice (DR); Fish and rice (FR); Ducklings, fish and rice (DFR); and layer ducks, fish and rice (LDFR). Rice yields were 8.6 and 15.0 % higher for the DFR and LDFR treatments, respectively, compared to rice only. Fish yields were 2222 kg/ha for the FR treatment, and more than double this value when ducks were included in the system (4639 and 4792 kg/ha for the DFR and LDFR treatments, respectively). Net economic benefits were 1.16, 8.51, 44.22 and 55.64 million VND/ha from the rice (R), Fish-rice (FR), Ducklings-fish-rice (DFR) and layer ducks-fish-rice (LDFR) systems, respectively. Maximum residue limits (MRL) of insecticides were 3.9 to 4.3 g / kg paddy and 0.05 g /litre water in the rice only treatment.
In
the North of Vietnam there is a serious problem of contamination of food for humans,
as well as feeds for animals, because of excessive use of insecticides,
especially in the rice crop. A preliminary
technical evaluation of the duck-rice system was carried out using 350 local
ducklings in a rice area of 0.504 ha. Replacing conventional fertilizer
application and weeding by growing ducklings (1,400 / ha) had no effect on rice
yield and resulted in reduced production costs, and complete elimination of insecticide residues
in the paddy rice.
The
main objective of the present study therefore was to evaluate different
strategies for reducing or even eliminating the use of insecticides for rice,
using local ducks in duck-rice and duck-rice-fish systems. It
is expected that this study will help extension staff, researchers, policy
makers and farmers to produce food and feeds not contaminated with
insecticides, thus improving both human and animal health.
There were in total
eight treatments (Table 1), with rice alone (R), with or without insecticide
application, and with one or two applications of fertilizer and weeding, or in
combination with ducks (DR).
|
Table 1. Design of experiment 1 |
||||||||
|
System |
Rice only (R) |
Ducklings -
Rice (DR) |
||||||
|
Plot |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
|
Ducklings / ha |
- |
- |
- |
- |
1000 |
1300 |
1600 |
1900 |
|
Fertilizer (no. of times) |
1 |
2 |
1 |
2 |
- |
- |
- |
- |
|
Weeding grass (times) |
1 |
2 |
1 |
2 |
- |
- |
- |
- |
|
Use insecticides |
yes |
yes |
- |
- |
- |
- |
- |
- |
At harvest, 5 samples
of rice (each from an area of 1 mē) were
taken from each of the four corners and the centre of each plot, and then dried
in the sun. The
concentrations of insecticides in the rice samples were determined at the Northern
Pesticide Control Centre (NPCC). Calculations were made of rice yields, duck
production, MRL (maximum residue limit) of insecticides and economic benefits
from the different systems.
The effects of
combining ducks with rice on rice yields and MRL are
shown in Table 2.
|
Table 2.
Effect of including ducks in rice fields on insecticide concentrations and
duck performance |
||||||||||
|
System |
Rice only (R) |
Ducklings - Rice (DR) |
||||||||
|
Plot |
1 |
2 |
3 |
4 |
X |
5 |
6 |
7 |
8 |
X |
|
Rice
yield (kg/ ha) |
4039 |
4081 |
3969 |
3964 |
4013 |
4056 |
4084 |
3989 |
3931 |
4015 |
|
Duck production |
|
|
|
|
|
|
|
|
|
|
|
Mortality (%) |
- |
- |
- |
- |
- |
2.8 |
2.5 |
2.6 |
2.1 |
2.5 |
|
Mean
live weight, g |
- |
- |
- |
- |
- |
1070 |
1080 |
1035 |
1020 |
1051 |
|
MRL (g / kg paddy) |
4.3 |
4.1 |
- |
- |
4.2 |
- |
- |
- |
- |
- |
The rice
yield was the same in the DR and R systems, and the ducklings had normal growth rates with
similar daily weight gains as in conventional intensive rearing systems.
Table 3.
Inputs and outputs for rice and for ducklings (Experiment 1; million VND /
ha)
|
||||||||||
|
System |
Rice only (R) |
Ducklings -
Rice (DR) |
||||||||
|
Plot |
1 |
2 |
3 |
4 |
X |
5 |
6 |
7 |
8 |
X |
|
|
|
|
|
|
|
|
|
|
|
|
|
For rice
|
5.03 |
5.86 |
4.75 |
5.58 |
5.31 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
|
For ducklings |
- |
- |
- |
- |
|
6 |
7.8 |
9.6 |
11.4 |
8.7 |
|
Total |
|
|
|
|
5.31 |
|
|
|
|
12.6 |
|
|
|
|
|
|
|
|
|
|
|
|
|
8.08 |
8.16 |
7.94 |
7.93 |
8.03 |
8.11 |
8.17 |
7.98 |
7.86 |
8.03 |
|
|
From ducklings |
- |
- |
- |
- |
|
10 |
13 |
16 |
19 |
14.5 |
|
Total |
|
|
|
|
8.03 |
|
|
|
|
22.5 |
|
|
|
2.72 |
|
|
|
|
9.91 |
|||
It
is concluded that ducks combined with rice eliminates insecticide residues
from paddy rice and gives substantially higher economic benefits to producers
compared to rice only. The system is particularly suitable for rice cultivation
on a small scale in the North of Vietnam, which is quite different from the
South. Because of the narrow fields between the villages, and the poor
fertility of the soil, ducks cannot be raised on a large scale,
and they are scavenging in the fields only during the daytime. At night, they are kept in shelters
and given supplementary feed. The densities of ducks in this trial varied from
0.10 to 0.19 ducks / mē (1 duck / 5 to
10 mē), which may not be suitable in the South of Vietnam, as in the Mekong delta a density of 1 duck /
18 mmē has been reported.
|
Table
4. Species and densities of fingerlings |
||||
|
Fish species
(position in pond)
|
Fingerlings |
Fingerling
size (cm) |
||
|
|
Numbers/ha |
Mean
weight (g) |
Harvest
twice/year |
|
|
Silver Carp, Tench
(top) |
1100 |
25 |
3 |
6 |
|
Black / White Carp (top) |
3100 |
- |
6 |
20 |
|
Tilapia, Major (middle) |
1400 |
25 |
3 |
6 |
|
Common carp (bottom) |
1100 |
25 |
3 |
6 |
|
Total |
6700 |
|
|
|
|
System |
Rice (R) |
Fish-Rice (FR) |
Duckling-Fish-Rice
(DFR) |
Layer duck-Fish-Rice
(LDFR) |
||||||
|
Plot |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
|
Ducklings / ha |
- |
- |
1000 |
1300 |
1600 |
1900 |
- |
- |
- |
- |
|
Layer ducks / ha |
- |
- |
- |
- |
- |
- |
400 |
600 |
800 |
1000 |
|
Use insecticides |
yes |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
System |
Rice (R) |
Fish-Rice (FR) |
Duckling-Fish-Rice
(DFR) |
Layer Duck-Fish-Rice
(LDFR) |
||||||||
|
Plot |
1 |
2 |
3 |
4 |
5 |
X |
6 |
7 |
8 |
9 |
10 |
X |
|
Rice yield (kg/ ha) |
4125 |
4195 |
4667 |
4500 |
4361 |
4387 |
4479 |
4722 |
4944 |
4750 |
4556 |
4743 |
|
Fish yield (kg/ha) |
- |
2222 |
3889 |
4278 |
4833 |
5556 |
4639 |
3889 |
4583 |
5000 |
5694 |
4792 |
|
MRL |
|
|
|
|
|
|
|
|
|
|
|
|
|
g / kg paddy |
4.2 |
- |
- |
- |
- |
- |
|
- |
- |
- |
- |
- |
|
g / litre water |
0.05 |
- |
- |
- |
- |
- |
|
- |
- |
- |
- |
- |
|
System |
(R) |
(FR) |
(DFR) |
(LDFR) |
||||||||||
|
Plot |
1 |
2 |
3 |
4 |
5 |
X |
6 |
7 |
8 |
9 |
10 |
X |
|
|
|
Inputs |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Rice
|
7.92 |
7.36 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
3.92 |
|
|
|
Fish |
- |
15.58 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
13.9 |
|
|
|
Ducklings |
- |
- |
6 |
7.8 |
9.6 |
11.4 |
8.7 |
- |
- |
- |
- |
- |
|
|
|
Layers |
- |
- |
- |
- |
- |
- |
|
30.24 |
45.36 |
60.48 |
75.6 |
52.92 |
|
|
|
Total |
7.92 |
22.94 |
|
|
|
|
|
|
|
|
|
70.74 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
|
Rice
|
9.08 |
9.23 |
10.27 |
9.9 |
9.59 |
9.65 |
9.85 |
10.39 |
10.88 |
10.45 |
10.02 |
10.44 |
|
|
|
Fish |
- |
22.22 |
38.89 |
42.78 |
48.33 |
55.56 |
46.39 |
38.39 |
45.83 |
50 |
56.94 |
47.92 |
|
|
|
Ducklings |
- |
- |
10 |
13 |
16 |
19 |
14.5 |
- |
- |
- |
- |
- |
|
|
|
Layers |
- |
- |
- |
- |
- |
- |
|
38.8 |
58.32 |
77.76 |
97.2 |
68.02 |
|
|
|
Total |
9.08 |
31.45 |
|
|
|
|
|
|
|
|
|
126.38 |
|
|
|
1.16 |
8.51 |
|
|
|
|
|
|
|
|
|
55.64 |
|
||
|
System |
(R) |
(FR) |
(DFR) |
(LDFR) |
|
|
Inputs |
|
|
|
|
|
|
For Rice
|
6.62 |
3.92 |
7.36 |
3.92 |
3.92 |
|
For
Fish |
- |
8.7 |
- |
8.7 |
52.92 |
|
For Duck |
- |
- |
15.58 |
13.9 |
13.9 |
|
Total |
6.62 |
12.62 |
22.94 |
26.52 |
70.74 |
|
|
|
|
|
|
|
|
From Rice |
8.56 |
8.03 |
9.23 |
9.85 |
10.44 |
|
From
Fish |
- |
14.5 |
- |
14.5 |
68.02 |
|
From Duck |
- |
- |
22.22 |
46.39 |
47.92 |
|
Total |
8.56 |
22.53 |
31.45 |
70.74 |
126.38 |
|
+1.94 |
+9.91 |
+8.51 |
+44.22 |
+55.64 |
|
This research was partially financed by the bilateral SAREC project 2000-2002.