Elkana Hezron and
Julius W Nyahongo, from the institute of Tanzania. wrote a Research
article about, Deadwood, Living Value: Acacia Litter and Biodiversity in
Central Tanzania. entitled, Quantification of deadwood littered by Acacia spp.
in semi-arid ecosystems of central Tanzania: . This research paper published by the Journal of Biodiversity and Environmental Sciences | JBES. an open access scholarly
research journal on Biodiversity. under the affiliation of the International
Network For Natural Sciences| INNSpub. an open access multidisciplinary
research journal publisher.
Abstract
Deadwood (DW) is an important carbon component for conservation and management of biodiversity resources. They are ubiquitous in many semi-arid ecosystems although its estimation is still posing lots of challenges. At Chimwaga woodland in Dodoma Region of Central Tanzania, seasonal quantification of DW produced by two Acacia spp. was done to evaluate the influence of each tree species, Dbh and canopy area on DW biomass and to determine their ecological role in conservation of semi-arid ecosystem. Both purposive and random sampling techniques were used in the course of a completely randomized design (CRD). Thirty trees from each species of Acacia tortilis and Acacia nilotica were studied. Results portray that DW biomass was significantly higher (P < 0.05) in the dry season than in the rain season whereby A. tortilis produced 669.0 ± 135.90kg DM/ha (dry season) and only 74.3 ± 135.90kg DM/ha (rain season) while A. nilotica produced 426.1 ± 135.90kg DM/ha (dry season) and 36.5 ± 135.90kg DM/ha (rain season). DW biomass did not correlate significantly (P > 0.05) with Dbh and canopy area. Inter-specific interactions were encountered from experimental areas where DW was littered that facilitated ecosystem balance in semi-arid areas. This information is important for estimating amount of dead wood biomass required to be retained in the forest provided that, at the expense of ecology, they are refuge for arthropods, fungi, bryophytes and other important soil microbes representing primary components of Biodiversity in semi-arid ecosystems.
Introduction
Natural treasures and
heritage such as those of semiarid areas rich in deadwood (DW) materials are
rapidly utilized and depleted by living organisms globally while facing an
extinction rate of about 100- 1000 times compared to the rate before 150,000
years ago of human life time (Baharul & Khan, 2010). Thousands of organisms
depend on DW as an important key for biodiversity in forest ecosystems (Harmon
& Sexton, 1996; Pyle & Brown, 1999). Africa and other continents such
as Australia and America are comprised of such resources at large although they
are faced with many challenges from anthropogenic activities (IUCN, 2017).
Tanzania in East Africa is one among rich countries in terms of natural
resources and biodiversity comprising semiarid woodlands (URT, 2014). Vast of
Ecological, environmental and botanical studies have been done purposely to
determine total area covered by forests, identify and estimate species
diversity, abundance and distribution (Malimbwi & Zahabu, 2014; Monela,
Chamshama, Mwaipopo, & Gamassa, 2005). Other studies are done to assess
ecosystem goods and services obtained from these resources (Dharani, 2006; FAO,
2010; Monela et al., 2005; Sharam, Sinclair, Turkington, & Jacob, 2009). In
disparity to the reported information, studies on DW production that estimate
the biomass in semi-arid areas are scarce. Fewer research reports are available
to describe the ecological importance contributed by DW and their role in
biodiversity conservation for prevalence of savanna dry lands as well as
sustainable use of forest products in semi-arid regions.
Earlier than 2007, many
communities around the world considered DW as of less significant in the
ecosystems (Stachura, Bobiec, Obidziñski, Oklejewicz, & Wolkowycki, 2007).
These resources were regarded as uneconomical, obstacles to silviculture and
reforestation that were reflected to a cause of abiotic disturbance that
threatened the health of terrestrial ecosystems by catching fire easily
(Pfeifer et al., 2015; Thomas, 2002; Travaglini et al., 2007; Travaglini &
Chirici, 2006). Additionally, stumps from dead trees seemed to be source of
injuries that endangered the public safety (Peterken, 1996; Thomas, 2002).
Dead Wood pieces and
stumps are cleared from forests as a sanitary strategy (WWF, 2004). Collections
of wood fuels increased from 243.3 million m3 (in 1990) to 313.9 million m3 (in
2005) in the Eastern and Southern African forests (Monjane, 2009). These
actions lowered the quantity of DW and their ecological significance in the
ecosystems (Travaglini et al., 2007). It is further reported that there were a
stable quantity of harvestable DW produced from 1992/93 to 1995/96 regardless
of partial variation from year to year in the African woodlands as indicated in
Table 1 (Collins, 1977; Malaisse, Alexandre, Freson, Goffinet, &
MalaisseMousset, 1972; Malaisse, Freson, Goffinet, & Malaisse-Mousset,
1975; Shackleton, 1998).
In recent years since
2000 up to date, conservationists have become alarmed about the role of DW in
the natural ecosystems (Rondeux & Sanchez, 2009; MCPFE, 2002; Humphrey et
al., 2004; Schuck, Meyer, Menke, Lier, & Lindner, 2004). Leaders in the
developed and developing countries are encouraged by the WWF to call foresters,
environmentalists, agriculturists and ecologists to conserve biodiversity by
increasing DW in the forests to 20-30 m3/ha by 2030 (WWF, 2004; Marage &
Lemperiere, 2005; Zielonka, 2006; Vandekerkhove et al., 2009; Humphrey &
Bailey, 2012).
It is reported that the
available information on DW production is limited to total harvestable and
standing DW with scarce data on the biomass produced by DW in semi-arid
ecosystems under the influence of natural factors (Malaisse et al., 1972;
Collins, 1977; Shackleton, 1998; Chojnacky & Heath, 2002; WWF, 2004).
Hence, the study aimed
to (1) quantify the amount of DW biomass produced by Acacia spp. during dry and
rain seasons, (2) evaluate the influence of each tree species, Dbh and canopy
area on DW biomass and (3) to determine the ecological role of DW in conserving
biodiversity of semi-arid ecosystem through provision of nutrients to
decomposers.
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