ArticlePDF Available

Investigation of survival rate of trees planted in agroforestry and forest plantations in Huye District from 2007 to 2011 and underlying factors

Authors:

Abstract and Figures

This study was conducted in Huye District from December 2011 to June 2012, with aiming to investigate the survival rate of trees planted on private and public land from 2007-2011 and underlying factors. Low survival rate of trees planted during annual planting campaigns is often reported in many parts of the country and there is need to understand why and propose adequate solutions to improve survival rate of trees in plantation. The study was conducted in three sectors of Huye District namely Mukura, Tumba and Ngoma sectors. Data were collected through a structured questionnaire that was administered to 51 sample farmers as well as through actual counts conducted both on private and public trees and forest plantations. The collected data were analysed and presented using SPSS and Microsoft Excel softwares. The results of the study revealed that, in the study area, the majority of trees fail to survive after the tree planting season generally due to lack or poor post-planting care. Thirty nine percent of respondents reported to have not provided any post-planting care to their trees. Nevertheless, 35% of respondents reported to have weeded their trees during the studied period. In addition, the results indicate that private trees survive better than public ones. The mean survival rate computed on a sample of agroforestry private trees was 51% while on public trees it was 30%. In woodlots and forest plantations, private trees survived at 65% while the public ones survived at 40%. This study should be carried out in other parts of the country in order to identify underlying factors behind low survival rate of trees after each tree planting season.
Content may be subject to copyright.
52 Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013
Rwanda Journal ISSN 2305-2678 (Print); ISSN 2305-5944 (Online)
DOI : http://dx.doi.org/10.4314/rj.v1i1.4E
Investigation of survival rate of trees planted in
agroforestry and forest plantations in HuyeDistrict from
2007 to 2011 and underlying factors
J. P. Murekezi, J. Nduwamungu and E. Munyanziza
Faculty of Agriculture,
National University of Rwanda
Corresponding Author: jnduwamungu@nur.ac.rw/jeanduwa@gmail.com
Abstract
This study was conducted in Huye District from December 2011 to June
2012, with aiming to investigate the survival rate of trees planted on private
and public land from 2007-2011 and underlying factors. Low survival rate of
trees planted during annual planting campaigns is often reported in many
parts of the country and there is need to understand why and propose
adequate solutions to improve survival rate of trees in plantation. The study
was conducted in three sectors of Huye District namely Mukura, Tumba and
Ngoma sectors. Data were collected through a structured questionnaire that
was administered to 51 sample farmers as well as through actual counts
conducted both on private and public trees and forest plantations. The
collected data were analysed and presented using SPSS and Microsoft Excel
softwares. The results of the study revealed that, in the study area, the
majority of trees fail to survive after the tree planting season generally due
to lack or poor post-planting care. Thirty nine percent of respondents
reported to have not provided any post-planting care to their trees.
Nevertheless, 35% of respondents reported to have weeded their trees during
the studied period. In addition, the results indicate that private trees survive
better than public ones. The mean survival rate computed on a sample of
agroforestry private trees was 51% while on public trees it was 30%. In
woodlots and forest plantations, private trees survived at 65% while the
public ones survived at 40%. This study should be carried out in other parts
of the country in order to identify underlying factors behind low survival rate
of trees after each tree planting season.
Keywords: Deforestation, reforestation, tree survival rate, tree planting
seasoning, physical count of trees.
Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013 53
1. Introduction
Deforestation has been going on in Rwanda since long time as forests
were cleared in favour of agriculture. However, during the last fifty
years, deforestation and forest degradation accelerated due to various
factors. Between 1960 and 2002, the area of natural forests of Rwanda
underwent a decrease of about 65% (Twagiramungu, 2006). The
search for arable lands, extensive farming, illegal felling of forests for
firewood, production of wood for charcoal and poles for building in
urban areas, as well as a land mismanagement have drastically
contributed to this reduction of natural forest coverage. Currently the
remaining natural forests are all protected and practically almost all
forest products needs are met through harvesting planted trees and
forests (ROR, 2010).
Nowadays, forest restoration is being addressed at the national and
international levels to restore previously depleted forests through
forest plantation establishment projects (Maginnis and Jackson, 2003;
Evans and Turnball, 2004). In Rwanda, every year, the government
with the support of various NGOs and development project donors,
spends a huge budget in forest restoration and rehabilitation through
production and distribution of tree seedlings throughout the country
(Nduwamungu, 2011). However, despite the great efforts invested in
mobilizing human and financial resources for tree planting during the
annual tree planting week and beyond, low survival rate of newly
planted trees and forests has been reported throughout the country
(ROR, 2010).Low survival rate of trees planted during community
works is common in many parts of the country and there is need to
understand why and propose adequate solutions to improve survival
rate of trees in reforested areas.
Huye District is one of the districts in which the issue of poor
establishment of newly planted trees has been widely observed as
indicated by the dominance of old forest plantations throughout the
District in comparison with the number of tree seedlings produced and
planted each year (HDESA, 2011). Thus, the objective of this study
was to investigate possible factors behind low survival rate of trees
after each tree planting season in Huye District and propose how to
54 Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013
ensure optimum establishment of man-made forests and agroforestry
trees.
2. Materials and Methods
This study was conducted within three sample sectors of Huye District
namely,Tumba, Ngoma and Mukura. In each sample sector, seventeen
respondents were randomly selected provided that they have planted
some trees between 2007 and 2011. A structured questionnaire
consisting of both open-ended and closed-ended questions was
prepared for data collection and was administered directly to 51
respondents while collecting also data on private trees and forests.
During interview, the questions asked focussed on total number of
trees planted by the respondent from 2007 to 2011(the species planted,
the type and source of planting materials, number that survived) and
on information about underlying factors that could influence the rate
of survival of newly planted trees such as tree planting method, tree
planting season, types and quality of seedlings used while planting,
aftercare activities done, seedling transportation method and handling,
control and monitoring of the planted trees.In addition, actual physical
count of surviving trees was carried out in randomly selected private
and public sites in the study area.
The physical count enabled estimation of the actual number of
surviving trees out of many planted either on private or public sites.
Through this count, each tree (s) reported to have been planted at any
site by each respondent was physically checked in order to ascertain
that the said trees were really planted and thereby being able to record
the reliable survival rate of trees on that site. Physical count also
helped identify the real species of the planted trees since some
respondents were not aware of tree species that were planted. Per each
site, only five transects were randomly selected for physical count, and
per each selected transect, both the number of empty holes and the
number of surviving trees were recorded. These records helped in
calculating the survival rate of trees per that site given that the total
number of planted trees was known. Figure1 is a sketch of how
physical count was carried out in the field. The Statistical Package for
Social Sciences (SPSS) and Microsoft Excel were used to process the
data.
Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013 55
Figure1: Graphical illustration of how physical count
was carried out in the field
Where: Lis length of the site,W is width of the site, isempty hole;
is surviving tree and T1, T2,…. T5are Transect numbers.
3. Results and Discussion
Source of tree planting stocks
All respondents reported that they use seedlings as the main tree
planting material. About 82% of respondents (Table 1) confirmed that
they use tree seedlings sourced from tree nurseries of administrative
Cells (“Pepiniyeriz’utugari”), suggesting that within Huye District,
seedlings distribution to the farmers generally occurs at the cell level.
Table 1: Source of tree planting stock
Source of planting stock
Frequency
(%)
Cell nursery
42
82.4
Sector nursery
4
7.8
Private nursery
3
6.0
Own nursery
1
2.0
Wildings
1
2.0
Tree planting period and techniques
About 82% of respondents reported that they planted their trees in
November which is the normal tree planting season. The greatest
proportion reported to dig planting pits one week before planting
(Table 2).Unless the pits are not deep enough this period is normally
56 Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013
about the right time to plant trees(the best being two weeks before
planting) (Nduwamungu, 2011). Nevertheless, it was reported that
seedlings are often transported by hands on open environment without
taking into account of potential sun heat damage which can increase
water loss by seedlings especially root desiccation (Landis and Haase,
2008) and later reduce survival rate of planted trees.
Table 2: Time of digging planting pits (N=51)
Time of digging
Frequency
Percentage (%)
The same day at the planting
period
10
19.6
A day before planting
4
7.8
Two days before planting
6
11.8
A week before planting
17
33.3
Two weeks before planting
8
15.7
More than two weeks before
planting
6
11.8
Post planting care conducted on newly planted trees
The majority of respondents (39%) reported that they do no post-
planting care to their trees. The trees are left on their own. Even
though 35% of farmers said that they carried out weeding, this
percentage is still at the lower end because weeding activity for tender
trees is known to be the most important post-planting care for
successful establishment of newly planted trees (Elefritzet al., 1998).In
fact, about 94% of respondents complained that after planting there is
no follow up of private trees and woodlots by forestry professionals in
the district. The care is all left to the farmer who is not even instructed
on proper tending techniques of young tree plantations. This is a great
challenge that should really be addressed if higher survival rate and
performance are to be achieved. Table 3summarises responses on the
follow up care provided to tender trees just after they are planted out.
Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013 57
Table 3: Post planting care conducted (N=51)
Frequency
Percentage (%)
20
39.2
18
35.3
6
11.8
2
3.9
3
5.9
1
2.0
1
2.0
Annual survival rate of trees from 2007 to 2011
The results of this study indicated that there is still a great amount of
trees which fail to establish just after they are planted out. This is
proved by the relatively low survival rates of many trees planted either
on private land or on public land (Figures 2, 3, 4 &5). Nevertheless,
comparing the survival rates on private and public lands, it was noted
that trees on private lands survive better than those planted on public
lands. In fact, basing the actual physical count in sample agroforestry
and forest plantation sites randomly selected in the study area, the
mean survival rate during the last five years (2007-2011) in
agroforestry on private lands was 51% while on public lands it was
30%. In woodlots and forest plantations, trees on private lands
survived at 65% while those on public lands survived at 40% (Figures
4 &5).
58 Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013
Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013 59
The difference in survival rates on private and public lands may
probably be attributed to inappropriate handling methods of seedlings
while planting. Foster and Blaine (1978) remarked that one tree
planting contractor lost 38% of sidewalks trees in Boston City in the
first year due to careless handling of plant material. Poor survival may
have resulted also from insufficient control and monitoring as well as
insufficient post planting care provided to the public trees on different
planting sites. This is because most public trees and forest plantations
are generally established during community works known as
Umugandarusange”. Even when some post-planting care activities
are undertaken on public lands, they are not properly done because
60 Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013
they are done during those community works by unskilled people
often without any guidance from forestry professionals
(Hategekimana, Forest extension officer, Pers. Communication).
4. Conclusion
This study has shown that a great number of trees fail to develop
properly after each tree planting season which results in poor
establishment of new forests in Huye District. Poor tree survival rate is
generally attributed topoor post-planting care whereby 39% of
respondents reported that they do not provide any post-planting care to
their trees. Trees are generally planted and left to grow on their own.
Nevertheless, some respondents (35%) reported to have carried out
some kind of weeding in their woodlots or for agroforestry trees. This
percentage is yet still inadequate since weeding is considered as one of
the most important post-planting carethat can lead healthy woodlots
and forestplantations with increased tree vigour and survival rate.
Meanwhile, it was revealed that trees on private land survived better
than those planted on public lands. Indeed, the mean survival rate of
51% in agroforestry on private land between 2007 and 2011was low
but higher than the mean survival rate of 30% found in agroforestry on
public land. In woodlots and forest plantations, private trees survived
at 65% while on public land trees survived at 40% on average from
2007 to 2011.
Basing on above findings, it should be recommended that tree planting
and tending activities during community works (Umugandarusange)
should be supervised by skilled workers, instead of leaving people on
their own without proper instructions on proper tree planting and
tending techniques. Local authorities should also organize regular and
supervised community works on each site where public trees have
been planted in order to ensure proper post-planting care which will
likely improve survival rate of planted trees. Furthermore, the forest
extension services should be strengthened in order to ensure adequate
farmer education and follow up of planted trees and forests.This study
should also be carried out in other parts of the country in order to find
out whether or not the underlying factors behind low survival rate after
each tree planting season in Huye District are similar to those in other
Districts.
Rwanda Journal, Series E: Agricultural Sciences Vol. 1 No. 1, 2013 61
References
1. Evans, J., and Turnbull, J. (2004).Plantation forestry in the
Tropics.Forest Nurseries.Oxford University Press. Oxford
2. Elefritz, M., Atkinson, M.M., and Fitzgerald, S.A. (1998).
Common mistakes while tree planting. Tree planting techniques,
p.8. Oregon
3. Foster, R. S. and Blaine, J. (1978). Urban tree survival: trees in the
sidewalk. Journal of Arboriculture 4(1): 14-17.
4. Huye District EDPRS Self-Assessment (HDESA), (2011).EDPRS
Self-Assessment Report, HuyeDistict, Huye.
5. Landis, T.D., and Haase, S. (2008). Maintenance of stocks
“Quality after they are harvested”.Forest Nursery Notes 28(14),
pp. 4. Washington, D.C.
6. Maginnis, S. and Jackson, W. (2003). The role of planted forests in
forest landscape restoration.
7. Nduwamungu, J. (2011). Forest plantations and woodlots in
Rwanda.African Forest Forum Working Paper Series, 1(14), 60p.
8. ROR (Republic of Rwanda), (2010). National Forestry
Policy.Ministry of Forestry and Mines, National Forestry
Authority, Kigali.
9. Twagiramungu, F. (2006). Reduction of the sizes of protected
areas in Rwanda and Reliance on biomass as the main source of
energy.Environmental profile of Rwanda, pp. 18-24. Kigali,
Rwanda.
... In an agroforestry system in Rwanda, the survival rate for Cedrela spp. and C. trichotoma was 60%, and the mean rate across the 14 studied tree species there was 51% [29]. Additionally, C. trichotoma survival reached 70% in our study, consistent with a previous report that its survival rate was higher than that of other species [68]. ...
... In our study, a crucial determinant of the survival of planted trees was browsing by cattle from neighboring farms, which affected 94% of the experimental plots. This highlights that proper management of livestock is essential in agroforestry [29]. For example, in Zambia, owners who controlled their livestock achieved survival rates of 68% in agroforestry systems, compared to only 32% on farms without this control [69]. ...
... This hypothesis was partially confirmed, since the type of plantation affected both survival and growth in Caaguazú, but it did not affect natural regeneration at either site. These results could be attributed to the following two factors: first, the scarcity of mother plants in the vicinity of the plots as sources of propagules [19]; second, the presence of livestock in the experimental plots due to a lack of local management [29]. ...
Article
Full-text available
The establishment of planted trees and the natural regeneration of trees in agroecosystems is challenging. This study evaluated the establishment and natural regeneration of the following six native tree species in two agricultural systems in the Atlantic Forest in Paraguay: Cedrela fissilis Vell., Cordia trichotoma (Vell) Arráb. ex Steud., Handroanthus albus (Cham.) Mattos, Handroanthus impetiginosus (Mart. ex DC.) Mattos, Peltophorum dubium (Sprengel) Taubert, and Cordia americana (L.) Gottschling and J.S.Mill. At the study site in Caaguazú, 18 plots of 100 m² each were established in 2 agronomic systems (conventional or agroecological) featuring 3 plantation types (pathsides, agricultural field edges, and islets). Trees were planted at this site in spring 2010 at a density of 1800 individuals ha⁻¹, and the site was monitored for six years. At the study site in Itapúa, 30 plots of 50 m² each were established in three agronomic systems (conventional, traditional, or agroecological). Trees were planted at this site in spring 2012 at a density of 1600 individuals ha⁻¹, and the site was monitored for four years. Survival and relative growth rates of the planted species and natural regeneration were analyzed using generalized linear mixed models that considered species, agronomic system, and plantation type as fixed factors, and time and plot as random factors. At both sites, survival varied among species. Here, C. fissilis showed lower survival and C. trichotoma higher growth than the other species. Naturally regenerated species were C. trichotoma, H. albus, and P. dubium. The agronomic system and species affected growth and natural regeneration at both locations. Plantation type affected survival and growth in Caaguazú only. We conclude that species contributes more than agronomic system or plantation type to determining the survival, relative growth rate, and natural regeneration in agroforestry systems in the Paraguayan Atlantic Forest.
... Using these vegetation indices in combination with, for example, a before/after control/impact type of designs [18,19] has been used to estimate the changes in greenness and vegetation productivity of projects with a known location. However, the lack of a complete and publicly accessible database of land restoration projects in Africa, the considerable number of organizations that work on this [1] and the reported low survival rates of planted vegetation [20][21][22][23], make these methods less suitable to evaluate the greening of land restoration projects and their climate change mitigation and adaptation potential on a continental scale. ...
Article
Full-text available
As a reaction to ongoing environmental change, many local land restoration projects have emerged that aim to prevent or reverse land degradation, combat climate change through carbon sequestration or improve the local climate. However, the contribution of these projects to the greening of Africa at larger scales is still unknown due to the absence of a (public) complete database of land restoration projects, the lack of monitoring and the low survival rate of planted vegetation. Here, we use climate independent greening time series to detect local greening hotspots in Africa. We find that 2.1% of Africa, an area of roughly 400000 km ² , experiences local greening, especially in semi-arid environments. We show that various forms of sustainable land management lead to significant local greening and demonstrate that some, e.g. active revegetation, are more effective than others, e.g. natural regeneration. This study, therefore, provides a first continental-scale insight in the greening potential of land restoration, which is needed for a thorough understanding of the effectiveness of sustainable land management.
... Given that the total number of planted trees was known, the survival rate of trees per arboretum was calculated for each species according to Murekezi et al. (2013). For each Eucalyptus species, five trees were randomly sampled. ...
Article
This study represents the first survey reporting the occurrence of Neofusicoccum species associated with Eucalyptus foliar diseases in semi-arid areas in North African countries. Based on morphological features and phylogenetic analyses of internal transcribed spacer (ITS) of nuclear ribosomal DNA (rDNA), translation elongation factor 1-alpha (TEF1) and β-tubulin (TUB2) genes, two species were identified: Neofusicoccum mediterraneum recovered from leaf spots on E. gillii in Tunisia and Neofusicoccum cryptoaustrale reported from leaf blight of E. torquata and E. odorata in Libya. Artificial inoculation trials on leaves confirmed the pathogenicity of the isolates to E. torquata, E. odorata and E. gillii. This report points out the threat posed by pathogens to non-native Eucalyptus in North Africa and suggests a likely movement of various pathogenic fungi from other hosts to Eucalyptus mainly E. ododrata trees that are totally infested by N. cryptoaustrale. Thus, it is recommended that E. odorata should not be planted in semi-arid areas. Further prospections of Eucalyptus arboretums are required to assess the incidence of foliar diseases on Eucalyptus plantations and to take appropriate and prompt measures against disease spread.
... However, over the last five decades, there were few success stories of such interventions due to the poor field survival rate of planted seedlings (Negussie et al. 2008). In many cases, the failure rate was so high (Cao 2008;Murekezi et al. 2013) that the achieved success from such interventions is lower than the resources invested in it. News articles that announce planting campaigns of millions of seedlings are common, the latest is the 4 billion trees campaign in Ethiopia to regreen the country and restore tree-based ecosystem functions and services. ...
Article
Full-text available
Tree planting is both a promising and controversial solution to climate change and biodiversity loss. However, this controversy is largely theoretical because we lack detailed information of how tree planting is proceeding on-the-ground. Here, we compiled a pantropical dataset of 174 tree planting organizations to determine the type of organizations involved in tree planting, their geographic locations and tree planting approaches. We found that the number of organizations have increased by 288% in the past 30 years, especially for-profit organizations. These organizations reported planting nearly 1.4 billion trees across 74 countries since 1961. Most frequently organizations reported establishing agroforestry systems or mixed species and single species plantations or using assisted natural regeneration, suggesting that tree planting programs are designed to support local communities as well as environmental objectives. Moreover, the most frequently reported species were commercial or utilitarian, with the top five including cacao, teak, moringa, mango and coffee. Finally, despite widespread efforts to plant more trees, there was a pronounced lack of monitoring on websites and in reports; only 18% of organizations mention monitoring at all, and only 5% mention measuring survival rate of plantings. Greater transparency and greater communication are needed between planting organizations and researchers to apply the most effective ways to restore forest cover. Further, while organizations often aimed to counter environmental problems, the use of the same sets of commercially useful species to meet economic development goals across the global indicates a need for greater coordination among organizations to avoid biotic homogenization.
Article
Full-text available
Deforestation and forest degradation have resulted in many impoverished landscapes worldwide that are characterised by a paucity of livelihood opportunities, drastically reduced biological diversity and diminished ecosystem functionality and productivity. Consequently, the restoration of forest functionality is important from both a socio-economic and environmental perspective inasmuch as it can enhance the contribution of natural resources to rural poverty reduction, increase the productive capacity and commercial viability of existing land-use systems, minimize long-term, environmental and economic risk, improve ecosystem services, ensure greater habitat connectivity and enhance biodiversity conservation. Although the conventional response of establishing planted forests as a counterweight to deforestation is seldom capable of restoring the multiple values that flow from natural forests or of adequately addressing all the needs of key interest groups, this paper argues that there is still a critical role for planted forests in restoring forest functionality at a landscape level. However in order to achieve this potential, and to move beyond the controversy that currently surrounds plantation forestry, it will be necessary for governments, the private sector and civil society to move beyond the "absolutist" rhetoric of entrenched positions. The true economic, societal and ecological utility of planted forests can only be determined when the broader context of the land use configuration within which they are located is properly considered. By focusing on the flow of forest goods and services at a landscape, or ecosystem, level rather than the nature of one particular land-use intervention at one particular site, disparate interest groups have a better starting point to negotiate how trade-offs between various land-uses can be best balanced to achieve an optimal outcome.
Common mistakes while tree planting
  • M Elefritz
  • M M Atkinson
  • S A Fitzgerald
Elefritz, M., Atkinson, M.M., and Fitzgerald, S.A. (1998). Common mistakes while tree planting. Tree planting techniques, p.8. Oregon
Maintenance of stocks "Quality after they are harvested
  • T D Landis
  • S Haase
Landis, T.D., and Haase, S. (2008). Maintenance of stocks "Quality after they are harvested".Forest Nursery Notes 28(14), pp. 4. Washington, D.C.
Forest plantations and woodlots in Rwanda
  • J Nduwamungu
Nduwamungu, J. (2011). Forest plantations and woodlots in Rwanda.African Forest Forum Working Paper Series, 1(14), 60p.
Reduction of the sizes of protected areas in Rwanda and Reliance on biomass as the main source of energy.Environmental profile of Rwanda
  • F Twagiramungu
Twagiramungu, F. (2006). Reduction of the sizes of protected areas in Rwanda and Reliance on biomass as the main source of energy.Environmental profile of Rwanda, pp. 18-24. Kigali, Rwanda.
Plantation forestry in the Tropics.Forest Nurseries
  • J Evans
  • J Turnbull
Evans, J., and Turnbull, J. (2004).Plantation forestry in the Tropics.Forest Nurseries.Oxford University Press. Oxford