ABSTRACT
This study was carried out to determine the effects of seed
desiccants, packaging materials and storage periods on seed quality and
longevity dynamics of three very important indigenous forest tree species. The
experimental period was December, 2015 to June, 2016. Seed collection was done
at the Bobiri Forest Reserve. The desiccation experiment was set up using a
Randomized Complete Block Design (RCBD) with three (3) replications for each of
the three species. The seed storage experiment was set up using 3 x 6 factorial
arrangements in Completely Randomized Design (CRD) with three replications for
each of the three species. Seed storage experiment was conducted using six
packaging materials (jute, nylon, paper, ziplock bag, airtight bottle and no
packaging) with three storage periods (no storage, three months storage and six
months storage). Germination percentage, seed vigour, 1000 seed weight,
moisture content, seed health analysis, carbohydrate, protein and oil contents
were assessed before storage, three and six months after storage. The study
revealed that the beads dried the seeds of Pericopsis elata within 2
days, 3 days to dry Sterculia rhinopetala seeds and 12 days to dry G.
cedrata, which was much faster than the rest of the desiccants without any
deleterious effect on seed quality and longevity. Pericopsis elata and Sterculia
rhinopetala showed orthodox seed storage behavior by surviving drying to a
lower moisture content hence improving storability when packaged in airtight
bottle (3.5%) and ziplock bags (3.5%) storage periods increased. The seed
carbohydrates, proteins and oils for Pericopsis elata and Sterculia
rhinopetala were maintained in the airtight packaging materials thereby
improving seed storability. The dormancy of Sterculia rhinopetala
was released by using GA3 with a germination percentage of 96.33%. Moist saw
dust significantly extended the life span of the Guarea cedrata seeds
for at least 21 days. A total number of nine fungi isolates were identified during storage. The seed viability equations predicted that P.
elata and S. rhinopetala seeds could be stored for 200 years and 177
years, respectively, after six months of storage. Seed viability dropped
significantly (155 days for P. elata and 79 days for S. rhinopetala)
after the accelerated aging test performed on the six-months old seeds. The
study concluded that P. elata and S. rhinopetala could best be
dried with beads at a faster rate and subsequently stored for a longer period
using airtight packaging materials whilst G. cedrata, could be stored in
a moist saw dust.
CHAPTER ONE
1.0 INTRODUCTION
Globally, the significance of
tropical forests is now well understood by scientists, politicians and people
of all races (Wagner and Cobbinah 1993; Goldsmith 1998; Verweij 2002). Tree
planting is undoubtedly, known to be an effective measure to protect the
climate and mitigate climate change. Trees sequester the greenhouse gas carbon
dioxide, counteract soil erosion and desertification (Grainger 1993). Trees act
as "carbon sinks" and absorb carbon from the air and change it into
plant material. That means that to a large extent, planting trees reduces
greenhouse gases in the atmosphere and significantly limit the rate at which
the ozone layer is depleted. Goods and services obtained from forests sustain
human life. Many forests serve as valuable biodiversity reservoirs. They
maintain the fertility and stability of agricultural lands, protecting the
natural watershed, serve as homes for countless wildlife, and habitats for some
cultures and communities. To be more precise, forests are natural assets of
huge importance (SCBD, 2009).
At an alarming rate, however,
forests are disappearing nearly one percent a year in sub-Saharan Africa (FAO,
2003), regardless of the many reforestation and conservation activities. Apart
from the major widespread environmental problems which include global warming,
flooding, food insecurity and loss of biological diversity, there is also
widespread concern for the 1.5 to 2 billion people who depend on trees for
livestock fodder, fruits, local construction, cooking and heating fuel (Bonner,
1992). The World Conservation Union (IUCN, 2008) UNEP WCMC (2001) estimated
that about 2000 tropical tree species in Africa are considered to fall into the
categories of being „near threatened‟ to „critically endangered‟.
High quality tree seeds are needed
to support both reforestation and the in and ex-situ conservation of forest
genetic resources (Schmit, 2000). There is therefore the greatest need to
restore degraded areas to improve their productive capacity, environmental
functions, and bio-diversity value (Parrotta, 2002). Persistent physical,
chemical, and biological factors are the major barriers that impede forest
regeneration, these severely degraded areas need human intervention to initiate
recovery. Among the many ecological restoration methods, planting of tree
seedlings have been identified as one of the effective measures to reforest
degraded lands (Lamb et al. 2005).
Annually, about one million
hectares (2.47 million acres) in the tropics are planted in tree seedlings, but
only a small percentage is indigenous (Bonner, 1992). According to Sacande et
al. (2004) information about the potential of indigenous species and the
availability of their seeds and seedlings are insufficient. Access to seeds and
seedlings come with seed handling and storage problems, which limit the use of
many high value indigenous trees in tree planting and conservation programmes
(Sacande et al. 2004). Furthermore, tropical forest seeds which show orthodox
seed storage behaviour have storage and dormancy related issues which adversely
affect their storability and seed quality. Such seeds quickly lose their
viability and vigour before the next planting season due to improper drying
methods, storage/packaging materials and poor storage conditions. Longer seed
storage durations also facilitate seed deterioration and reduce seed longevity.
The three selected important economic indigenous species for this study are; Peripcopsis
elata (Kokrodua) which is an endangered species (IUCN, 2008), Sterculia
rhinopetala (Wawabima) and Guarea cedrata (Kwabohoro) which have been described
as vulnerable, according to the IUCN Red List of Threatened Species (IUCN,
2001). These species therefore require urgent conservation attention.
It is an undeniable fact that, the
starting material for reforestation is seed. It is also the most useful
material for plant conservation purposes. Very high quality tree seeds are
required for Ghana to reach the target of the Forest Plantation Strategy
launched in 2013. This Programme was aimed at planting many hectares of forest
each year throughout the country up to the year 2050, with vigourous indigenous
and exotic tree species (Ghana Forestry Commission, 2013). From the foregoing,
if indigenous species are to be used in afforestation and conservation
programmes, it is important to gather relevant scientific knowledge on their
seed physiology, identify the appropriate responses of their seeds to
desiccation, dormancy breaking methods, storage potential, as well as their
seed health improvement techniques. The use of beads, silica gel, calcium chloride,
charcoal and rice have been widely used on agricultural seeds with quite an
appreciable success (Probert, 2003; Rao et al., 2006; Hay et al., 2012) but
scanty research information is reported on tree seeds . Storage life of seeds
(longevity) has also been improved by using different packaging materials like
jute, nylon, paper bags and airtight containers. There is therefore the need to
conduct research on the effects of desiccants, packaging materials and storage
periods on seed quality and longevity dynamics of these species. The study
primarily is aimed at contributing to scientific information on the effects of
seed desiccants and storage packaging materials on seed quality and longevity
dynamics of three indigenous forest tree species.
The specific objectives of the
study were:
i. To determine the effects of seed
desiccants on seed physical quality and chemical characteristics
ii. To determine the interactive
effects of packaging materials and storage periods on seed quality and
proximate composition
iii. Evaluate the most effective
dormancy breaking methods and moist storage on Sterculia rhinopetala and Guarea
cedrata seeds respectively.
iv. To
predict the longevity of the species using the Improved seed Viability Equation
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