25
populations were established in the fields at the time of plant-
ing, than in fields where maize followed on other crops, but de-
pending on wastage that had occurred at the previous harvests.
In maize following maize plantings, where harvest wastage in the
form of cobs and kernels was evident, relatively large established
colonies that increased after planting, were noted (
Photo 3a
and
Photo 3 b
). High populated areas severely affected maize at plant-
ing, necessitating replant.
Large gerbil colonies in fallow land following on maize dwindled
to negligible numbers at the start of the new planting season. A
maize trial planted in a fallow field had no gerbil damage in the
2014/2015 season.
To determine gerbil diet through stomach content analysis, High-
veld and Bushveld gerbils were collected in new maize fields
where groundnuts were planted the previous season, in new
groundnut fields following on maize, and in natural vegetation
adjacent to crop fields, for a period of one year.
The Highveld gerbil mainly fed on seeds at the planting, the veg-
etative growth stage of the crop, and at harvesting, while those
gerbils collected from natural vegetation included insects in their
diet in mid and late summer. The Bushveld gerbil’s diet in the
maize and groundnut crop fields at planting consisted of seed and
herbage, and included insects during high summer. The diet of
gerbils in the new groundnut fields, consisted of seeds through-
out the season until harvest.
Maize fields where livestock grazed after harvest had lower gerbil
populations and smaller gerbil colonies at the start of the new
planting season, than fields adjacent not used for grazing.
Maize fields where fallen cobs were collected by hand before and/
or after harvest, had lower incidences of gerbil activity at the start
of the new planting season.
At the Ottosdal study site, research on the effectiveness of barn
owls in the control of rodents, ten breeding pairs of barn owls
in nest boxes were monitored for a period of nine months. The
ten pairs constantly occupied the nests and most bred twice in
the study period. It was estimated that the ten pairs were able to
consume 14 600 rodents in a year.
Conclusion and suggestions
The Highveld gerbil and the Bushveld gerbil are indigenous and
common to most of the summer rainfall region of South Africa.
Food availability during winter determined the gerbil colony size
at the start of the new planting season. The food abundance in
field at this stage, whether maize or groundnuts, is determined
by the amount of wastage that occurred during harvest. The re-
striction of wastage, removal of fallen maize cobs, and grazing
reduces the food available for gerbils to sustain large populations
and limits the extension of the breeding season.
Encourage predators of gerbils by allowing for areas of natural
vegetation, and providing breeding sites and raptor perches.
Although maize seed treatment with zinc phosphide was effec-
tive in reducing the impact of gerbil damage on maize at planting
(
SA Graan/Grain
, October 2014), zinc phosphide cannot be used
pending registration. The only alternative for gerbil control is ro-
denticide bait registered for the use against gerbils in crop fields.
Rodenticide as burrow baiting must be applied to infested fields
and headlands over a three week period with three
applications at seven day intervals, preferably
three to four weeks before planting, with follow-up
baiting where activity persists.
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2016/CORP/A/016A
GEWASSE VIR ’N
VOLHOUBARE
TOEKOMS.
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