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J. Bio. Env. Sci. 2018
1 | Kwenye and Mwango
RESEARCH PAPER OPEN ACCESS
Lessons for REDD+ implementation: Insights from assessment
of forest governance in the joint forest management system in
Zambia
Jane Musole Kwenye*1
, Nelly Chunda-Mwango2
1
School of Natural Resources, Copperbelt University, Jambo Drive, Riverside, Kitwe,
Kitwe, Zambia
2
School of Built Environment, Copperbelt University, Jambo Drive, Riverside, Kitwe,
Kitwe, Zambia
Article published on February 18, 2018
Key words: REDD+, Forests, Forest governance, Joint forest management, Greenhouse gas emissions
Abstract
To draw lessons for informing strategies for reducing emissions from deforestation and forest degradation and
fostering conservation, sustainable management of forests and enhancement of forest carbon stocks (REDD+),
this study assessed community members’ perceptions of the quality of forest governance in the joint forest
management program relative to the ideal forest governance quality using the Katanino Joint Forest
Management study area in Zambia. The study focused on six elements of good governance, namely
participation, transparency, accountability, equity, efficiency and effectiveness. Using a two stage sampling
procedure, data for this study was collected using questionnaires administered to 120 randomly selected
community members who participated in the Joint Forest Management program in Serenje, Biwa and Bwengo
villages of Katanino Joint Forest Management pilot area. Results showed considerable gaps between ideal
quality of forest governance and the perceived quality of forest governance. One sample t-test results showed
that the perceived quality of all the six governance elements were statistically different from the ideal quality of
forest governance at the 95 % confidence interval, participation (t (119) = -76, ρ < 0.05), transparency (t (119)
= -130, ρ < 0.05), accountability (t (119) = -82, ρ < 0.05), equity (t (119) = -53.47, ρ < 0.05), effectiveness (t
(119) = -60, ρ < 0.05), efficiency (t (119) = -87, ρ < 0.05). Implications of these findings are highlighted
through a governance lens to inform strategies for REDD+ implementation.
*Corresponding Author: Jane Musole Kwenye  jane.kwenye@yahoo.com
Journal of Biodiversity and Environmental Sciences (JBES)
ISSN: 2220-6663 (Print) 2222-3045 (Online)
Vol. 12, No. 2, p. 1-10, 2018
http://www.innspub.net
J. Bio. Env. Sci. 2018
2 | Kwenye and Mwango
Introduction
Reducing emissions from deforestation and forest
degradation and fostering conservation, sustainable
management of forests and enhancement of forest
carbon stocks (REDD+) has emerged as a key
international strategy to halt land-use related
emissions in developing countries (Corbera and
Schroeder, 2011; Leventon et al., 2014; Matakala,
2016). A central tenet of the REDD+ mechanism
involves performance-based payments that
incentivize reductions in greenhouse gas (GHG)
emissions from deforestation and forest degradation
(Sekeleti, 2011). It is envisaged that well-designed
REDD+ mechanisms will have positive effects on
biodiversity, ecosystem conservation and the
livelihoods of forest-dependent communities
(Broekhoven et al., 2012; Kokwe, 2012). While
REDD+ is intended to prevent forest loss (Leventon
et al., 2014) and is not primarily a governance reform
per se, it is argued that it will affect or could be
affected by existing forest governance to a
considerable extent (Iqbal and Hussain, 2013; Larson
and Petkova, 2011).Moreover, in the recent past, the
‘writings’ on REDD+ mostly stress the need to focus
on governance issues (Gregersen et al., 2010; Cobera
and Schroeder, 2011) given that increasing the quality
of governance tends to be associated with a decrease
in deforestation rates and long-term carbon storage
globally (Umemiya et al., 2010).Thus, to draw lessons
for informing strategies for REDD+ implementation,
this study assessed community members’ perceptions
of the quality of forest governance in the joint forest
management program relative to the ideal forest
governance quality using the Katanino Joint Forest
Management study area in Zambia.
The Republic of Zambia is one of the developing
countries piloting the UN-REDD programme, which
is aimed at preparing countries for REDD+
implementation by building institutional and
technical capacity (Matakala, 2016). As part Zambia's
participation in the UN-REDD programme (Leventon
et al., 2014), Joint Forest Management (JFM) has
been identified as a forest management approach for
implementing REDD+ (UNDP et al., 201; Kokwe,
2012).
JFM is a forest management strategy under which the
government represented by the Forestry Department
and the local communities living adjacent to the local
forests enter into an agreement to jointly protect and
manage forests while sharing responsibilities and
benefits (Kokwe, 2012; Matakala, 2016). The JFM
approach enables local communities, by virtue of
their rights over land, to invest in and derive benefits
from the sustainable management and utilization of
forest resources in their area (Mbewe, 2007).
Forest governance arrangements that determined
how central questions regarding forests, livelihoods
and sustainability have been answered to date will
also determine how they will be answered under
REDD+ (Larson and Petkova, 2011). Thus, lessons
and experiences from previous forest-related
initiatives explored through a governance lens
(Kanowski et al., 2011) are critical for informing
strategies for REDD+ implementation. Identifying
governance gaps (Pedroni et al., 2009) in previous
forest-related initiatives in ways that are consistent
with the principles of good forest governance is
essential for REDD+ success (Kanowski et al., 2011).
However, comprehensive studies focused on drawing
lessons and experiences from JFM to inform
strategies for REDD+ initiatives through a
governance lens are rare in Zambia. Therefore, to
address this gap, this study was aimed at assessing
perceptions of the quality of forest governance in the
joint forest management program relative to the ideal
forest governance quality using the Katanino Joint
Forest Management pilot area in view of informing
strategies for REDD+ implementation. The study
focused on six elements of good governance namely
participation, transparency, accountability, equity,
efficiency and effectiveness. This is because good
forest governance is associated with structures and
processes that ensure multi-stakeholder participation,
accountability of actors and decision makers,
transparency of decision- making, efficient and
effective management of forest resources, as well as
fair and equitable allocation of resources and benefits
(Larson and Petkova, 2011; Sekeleti, 2011).
J. Bio. Env. Sci. 2018
3 | Kwenye and Mwango
Material and methods
Study site
The Katanino JFM pilot area lies 80 km from Ndola
and is traversed by the Ndola-Kapiri Road, the main
highway that links Copperbelt Province to Lusaka, the
nation's capital. Situated in Masaiti District in the
Copperbelt Province of Zambia, Katanino JFM pilot
area constituted one of the seven JFM pilot sites
under the Provincial Forestry Action Programme
(kokwe, 2012; Matakala, 2016). Villages situated in
close proximity to Katanino Local Forest, with a
population size of 3,842, were organized into four
zones for purposes of JFM piloting. Katanino JFM
area was chosen as a case study because it represents
a hotspot endowed with richness of complex data
ideal for governance exploration critical for informing
strategies for REDD+ implementation.
Notwithstanding the restriction of generalizing the
findings of this study to other JFM areas, results of
this highlight the governance issues that need to be
considered in each context.
Research instrument
The questionnaire used in this study contained
indicators reflecting elements of good governance
(FAO &PROFOR, 2011). The elements included
accountability, effectiveness, efficiency, equity,
participation and transparency. These elements were
chosen because they are comprehensive in nature and
have a global relevancy (Iqbal and Hussain, 2013).
Each element was measured using six indicators
which represented differing facets of the elements to
obtain a more well-rounded perspective of the
elements (Hair et al., 2010).Modified to suit the local
context, the indicators were adopted from Giri
(2006), Gyawali (2009) and Iqbal and Hussain
(2013). The indicators were scaled on a four-point
Likert scale, 1 to 4 in an increasing order of poor,
medium, good and excellent forest governance
quality. Score 4 on the scale represented the ideal
forest governance level. The questionnaire was
pretested on 15 community members who
participated in the JFM program in Serenje, Biwa,
and Bwengo Villages in April 2017.
Reliability assessment results showed that the
indicators used to measure perceptions of
participation, transparency, accountability, equity,
effectiveness and efficiency had acceptable internal
consistency with Cronbach's alpha ranging from 0.8
to 0.85. All items in the questionnaire were retained
although some items were slightly modified in
wording to improve comprehensiveness based on
feedback from the pretest.
Sampling design and sample size
A two-stage sampling procedure was used in this
study. In the first stage, three of the four villages
organized during piloting the JFM program were
randomly selected given that organization of the four
villages was done arbitrarily (Umar and Vedeld,
2012). In the second stage, participants from three
villages who participated in the JFM program were
selected using simple random sampling.
The minimum sample size for this study was
determined using the confidence interval approach
(Burns and Bush, 1995; Kwenye and Freimund,
2016). To obtain a 90% desired accuracy at the 90%
confidence level with the response and usable rates
set at 70 % and 10 % respectively, the required
minimum sample size was 110. A total of 120
community members who participated in the
Katanino JFM program were randomly selected in
Biwa, Bwengo and Serenje villages. Data for this
study was collected in April and May 2017.
Data analysis
Data for this study was analyzed using STATA 13.0
and Excel. Gap analysis, One-sample t-test and
analysis of variance (ANOVA) at a significance level of
ρ ≤ 0.05 were used to analyze the survey data. One
sample t-test was conducted to determine whether
the perceived quality for each of the six elements of
forest governance were statistically different from the
ideal quality of forest governance. Consequently, the
mean score for each of the six elements of forest
governance were compared with the mean score of 4
and six null hypotheses were tested: (i) H0: actual
mean scores of participation = ideal mean score of 4,
J. Bio. Env. Sci. 2018
4 | Kwenye and Mwango
(ii) H0: actual mean scores of transparency = ideal
mean score of 4, (iii) H0: actual mean scores of
accountability = ideal mean score of 4, (iv) H0: actual
mean scores of equity = ideal mean score of 4, (v) H0:
actual mean scores of effectiveness = ideal mean score
of 4, and (vi) H0: actual mean scores of efficiency =
ideal mean score of 4.
The one way ANOVA was conducted to determine if
there were statistically significant differences in the
mean of respondents' scores (i.e. actual mean scores)
for participation, transparency, accountability, equity,
effectiveness and efficiency based on the three villages
- Serenje, Biwa and Bwengo. Gap analysis between
respondents’ scores on the quality of forest
governance and the score for the ideal quality of
forest governance was undertaken using the spider
chart, mean scores and percentages.
Outliers and distribution of all measured variables
were examined to purify the data and reduce
systematic errors. Normality assessment results
showed that the data did not deviate from
multivariate normality. Outlier detection results
showed that there were no outliers in the data.
Results and discussion
Demographic characteristics of study sample
General demographic characteristics of the study
sample are provided in Table 1.
Table 1. General demographic characteristics of study sample.
Characteristic Percentage
Sex
Female 60.0
Male 40.0
Age
40-45 37.5
46-55 38.3
56-65 22.5
> 66 1.7
Annual household income
< K10,000 75.0
K10,000 - K20,000 25.0
Education level
Primary 57.0
Secondary 43.0
An analysis of the study sample shows that males
were in the majority (60 %) with the most
represented age group being 46-55 years old (38%).
The results also showed that majority of the
respondents earned less than K10, 000 annually
(75 %).
Summary statistics of respondents’ perception of the
quality of forest governance
Summary statistics for respondents’ perceptions of
the quality of the six forest governance elements are
provided in Table 2.Participation had the highest
mean score of 2.79, while equity had the lowest mean
score of 2.01.
J. Bio. Env. Sci. 2018
5 | Kwenye and Mwango
Table 2. Summary statistics for the governance elements.
Forest governance element Mean SD
Participation 2.79 0.17
Transparency 2.31 0.14
Accountability 2.02 0.23
Effectiveness 2.44 0.28
Equity 2.01 0.41
Efficiency 2.42 0.20
A comparison of respondents’ mean scores and the
ideal score of 4 representing good forest governance
showed that respondents’ mean scores for all the six
elements of forest governance were below the ideal
score (Table 3).
Table 3. Comparison of ideal and actual quality of forest governance elements: Achievement and gap analysis.
Elements of Forest
Governance
Mean score
(Ideal)
Mean score
(Actual)
Achievement (%) Gap (%)
Participation 4 2.79 69.75 30.25
Transparency 4 2.31 57.75 42.25
Accountability 4 2.02 50.50 49.50
Equity 4 2.01 50.25 49.75
Effectiveness 4 2.44 61.00 39.00
Efficiency 4 2.42 60.50 39.50
Comparison of actual and ideal forest governance by
achievement and gap analysis
Gap analysis results showed that respondents’ actual
scores for equity had the largest variance from the
ideal score for good forest governance (49.6%) while
participation had the smallest variance (30.3%).
In terms of closeness to the ideal standard for good
forest governance, the achievement analysis results
showed that participation had the highest
achievement (69.8%) while equity had the lowest
achievement (50.3%).
Table 4. Mean score and a comparison of ideal and actual quality of forest governance elements in Serenje, Biwa
and Bwengo villages: Gap analysis.
Elements of Forest
Governance
Serenje Village Biwa Village Bwengo Village
Mean score
(Actual)
Mean score
(Ideal)
Gap (%) Mean score
(Actual)
Mean score
(Ideal)
Gap (%) Mean score
(Actual)
Mean score
(Ideal)
Gap (%)
Participation 2.79 4 30.3 2.79 4 30.3 2.78 4 30.5
Transparency 2.33 4 41.8 2.31 4 42.3 2.31 4 42.3
Accountability 2.04 4 49.0 2.03 4 49.3 1.99 4 50.3
Equity 2.02 4 49.5 1.98 4 49.5 2.04 4 49.0
Effectiveness 2.45 4 38.8 2.42 4 39.5 2.45 4 38.8
Efficiency 2.42 4 39.5 2.44 4 39.0 2.41 4 39.8
This is finding is consistent with the spider web chart
results in Figure 1 which showed that respondents’
mean score for participation had the smallest gap
from the ideal score for good forest governance while
equity had the largest gap. Similarly, as shown in
Table 4, gap analysis results for Serenje, Biwa and
Bwengo villages showed that the respondents’ mean
scores for each of the six elements of good forest
J. Bio. Env. Sci. 2018
6 | Kwenye and Mwango
governance were below the ideal score of 4.
Additionally, for all the three villages, results showed
that participation had the smallest variance from the
ideal score for good forest governance. Overall, an
analysis of respondents’ mean scores and the gap
analysis results showed that respondents perceived
good forest governance to have been reflected more
through participation, effectiveness and efficiency
than through equity, accountability and transparency.
This finding is in contrast with Iqbal and Hussain
(2013) whose results showed that good forest
governance was reflected more through transparency
and equity than through participation and
effectiveness using a Pakistan setting.
Table 5. ANOVA results for statistical differences between groups: Serenje, Biwa and Bwengo villages.
Element Source DF SS MS F ρ
Participation Between groups 0.005 2 0.003 0.09 0.914
Within groups 3.603 117 0.031
Total 3.609
Transparency Between groups 0.014 2 0.007 0.36 0.697
Within groups 2.319 117 0.020
Total 2.333
Accountability Between groups 0.054 2 0.027 0.49 0.612
Within groups 6.421 117 0.054
Total 6.475
Effectiveness Between groups 0.020 2 0.010 0.12 0.886
Within groups 9.563 117 0.082
Total 9.583
Equity Between groups 0.060 2 0.030 0.18 0.838
Within groups 19.672 117 0.168
Total 19.731
Efficiency Between groups 0.018 2 0.009 0.23 0.795
Within groups 4.591 117 0.039
Total 4.609
Comparison of respondents’ perceptions of the
quality of forest governance across the three villages
Table 5 showed that for all the six elements there
were no statistical differences between respondents’
perceptions of the quality of forest governance in the
three villages namely Biwa, Serenje and Bwengo at
the 95 % confidence interval. Thus, it has been
demonstrated that perceptions of respondents were
consistent across the villages. Results of this study are
in line with Iqbal and Hussain (2013) who also
reported consistence of the perceptions of their
respondents using a Pakistan setting.
Comparison of actual and ideal quality of forest
governance
Table 6 showed results of the comparison of the mean
ideal score and the mean scores for each of the six
elements of forest governance. The results showed
that respondents’ mean scores for the six elements
were statistically different from the ideal mean score
of 4 at the 95 % confidence interval. Therefore, all the
six null hypotheses tested in this study are rejected.
Rejection of the null hypotheses has demonstrated
that the perceived quality of each of the six elements
of forest governance differed from the ideal quality of
each of these elements.
J. Bio. Env. Sci. 2018
7 | Kwenye and Mwango
Lessons for REDD+ implementation in Zambia
Empirical evidence in this study has shown that
respondents perceived the quality of forest
governance in the JFM program to be lower than the
ideal quality of good forest governance. That is, all the
six elements of good forest governance were
perceived to be lower than the ideal quality of good
forest governance. Consequently, this study’s finding
provides lessons for REDD+ implementation in
Zambia. Specifically, it reveals the need for forest
governance reforms when employing the JFM model,
in particular around mechanisms for equitable
decision making processes, as well as mechanisms for
fostering and strengthening transparent and
accountable institutions and decision making
processes. Forest governance reforms tailored to
addressing equity require ensuring that all the
stakeholders, particularly the most vulnerable have
the opportunity to participate in the decision making
process. Moreover, their interests need to be
considered by decision makers in the decision making
process.
Table 6. One sample t-test results.
Element Mean SD t-value DF ρ
Participation 2.79 0.17 -76.27 119 0.000
Transparency 2.32 0.14 -130 119 0.000
Accountability 2.02 0.23 -91.94 119 0.000
Equity 2.01 0.41 -53.47 119 0.000
Effectiveness 2.44 0.28 -60.10 119 0.000
Efficiency 2.42 0.20 -87.89 119 0.000
With regards to accountability, reforms should be
tailored to establishing mechanisms that ensure that
institutions with decision making authority have an
obligation to report, explain and be answerable for
the consequences of decisions they make. Such
mechanisms include, for example, establishing clear
criteria for evaluating the performance of decision
makers. Furthermore, establishing internal and
external audits to provide checks and balances is
critical for fostering accountability. Linked with
accountability is the issue of transparency (DESA,
2009). Transparency in decision making is
considered as an important factor in improving the
ability of stakeholders to hold key decision makers
accountable for their actions (Broekhoven et al.,
2012). Moreover, it helps to build trust between
stakeholders and break down barriers between
historically opposed parties (Sekeleti, 2011). Results
of this study have shown that if the JFM model is to
be used to implement REDD+ strategies, there is
need to ensure that stakeholders, particularly the
local communities follow and understand the decision
making process.
This requires involving them at every stage of the
decision making process. Further, clarity on how and
why decisions are made is fundamental for fostering
transparency. This requires ensuring that information
on decisions and the decision making processes are
available and accessible by all the stakeholders
(DESA, 2009).
Safeguards intended to ensure that REDD+ delivers
win-win scenarios whereby forests are conserved
alongside community development (Harvey et al.,
2010; Kelly, 2010) include requirements for full and
effective participation of relevant stakeholders
including local communities (UNFCCC, 2010). A
critical aspect that fosters participation is the
involvement of multi-stakeholders in the decision
making process. Therefore, if JFM is to be used as a
model for delivering REDD+ with safeguards, greater
attention must be paid to strengthening multi-
stakeholder participation. This necessitates the need
to avoid peripheral involvement of sectors that
influence forest management such as agriculture and
energy among others.
J. Bio. Env. Sci. 2018
8 | Kwenye and Mwango
Enhanced intersect oral collaboration linked to village
and forest area management governance structures is
fundamental in view of considering REDD+ within
the wider livelihood activities of forest communities
(Leventon et al., 2014). Such an endeavor requires
developing sustained structures for intersect oral
collaboration. Intersect oral collaboration is
fundamental in ensuring that REDD+ creates
incentives that ensure lasting and achievable
emission reductions while maintaining and
improving other ecosystem services that forest
provide (Sekeleti, 2011).
Forest governance reforms will need to be
complemented by reforms across sectors that affect
forests. This is because policies outside the forestry
sector have a significant impact on forests
(Broekhoven et al., 2012; Sekeleti, 2011).
Furthermore, the governance reforms will need to be
supported by implementation actions at the village
level in order for REDD+ to be an opportunity for
delivering community benefits (Leventon et al.,
2014). Moreover, designing transparent financial
structures for the performance-based implementation
of the REDD+ strategy that allows for an equitable
distribution of benefits is critical. Additionally,
understanding the community context and the way
that the design of REDD+ initiatives fits to this
context as well as the role of the broader policy
context in shaping support for JFM operations is
fundamental.
Fig. 1. Comparison between actual and ideal scores for six elements of good forest governance.
Implementing the elements of good forest governance
needs to begin with defining priorities as well as a
sequence for Zambia to develop the capacity of
stakeholders to administer the components of good
governance. Furthermore, a strategic and practical
approach to improving governance should be
dynamic and responsive to emerging topics and
interests (Broekhoven et al., 2012). In this regard,
what may be considered as the focus of governance
reforms currently should not be considered 'good
enough’ a number of years from now. Rather, it
should be viewed as part of a planning process on
how to move forward and build on achievements. In
addition, there is need to promote forest governance
monitoring which will aid in making changes that
respond to new priorities, address new weaknesses
and build on new strengths.
J. Bio. Env. Sci. 2018
9 | Kwenye and Mwango
Conclusion
This study has shown considerable gaps between the
ideal quality of forest governance and the perceived
quality of forest governance. Among the six elements
of forest governance, equity had the largest variance
from the ideal quality of forest governance (49.6%)
followed by accountability (49.5%) and transparency
(42.3%) with participation had the smallest variance
(30.3%). Achievement analysis showed that
participation had the highest achievement (69.8%)
followed by effectiveness (61%) and efficiency (60.5%)
with equity had the lowest achievement (50.3%).
For all the six elements there were no statistical
differences between the perceptions of respondents in
the three villages namely Biwa, Serenje and Bwengo
at the 95 % confidence interval, participation
(F(2,117) = 0.09, p = .913), transparency (F(2,117) =
0.36, p = 0.697) , accountability (F(2,117) = 0.49, p =
0.612), equity (F(2,117) = 0.18, p = 0.838),
effectiveness (F(2,117) = 0.12, p = 0.886) and
efficiency (F(2,117) = 0.23, p = .795). Thus, the study
has shown that respondents' perceptions of the
quality of forest governance as reflected by
participation, transparency, accountability, equity,
effectiveness and efficiency were consistent across the
three villages.
The perceived quality of all the six governance
elements were statistically different from the ideal
quality of forest governance at the 95 % confidence
interval, participation (t (119) = -76, ρ < 0.05),
transparency (t (119) = -130, ρ < 0.05), accountability
(t (119) = -82, ρ < 0.05), equity (t (119) = -53.47, ρ <
0.05), effectiveness (t (119) = -60, ρ < 0.05), and
efficiency (t (119) = -87, ρ < 0.05).Therefore, the
study has shown that the perceived quality of each of
the six elements of forest governance differed from
the ideal quality of each of these elements.
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property regime change? The Open Forest Journal 5,
42-52.
UNDP, UNEP, FAO, Government of Zambia.
2010. UN collaborative programme on Reducing
Emissions from Deforestation and Forest
Degradation in Developing countries, National Joint
Programme Document. UN-REDD programme.
UNFCC. 2010. The Cancun Agreement: Outcome of
the work of the Ad Hoc working group on long term
co-operative action under the convention, in: UNFCC
(Ed.), UNFCC/CP/2010/7/Add.1.

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Lessons for REDD+ implementation: Insights from assessment of forest governance in the joint forest management system in Zambia - JBES

  • 1. J. Bio. Env. Sci. 2018 1 | Kwenye and Mwango RESEARCH PAPER OPEN ACCESS Lessons for REDD+ implementation: Insights from assessment of forest governance in the joint forest management system in Zambia Jane Musole Kwenye*1 , Nelly Chunda-Mwango2 1 School of Natural Resources, Copperbelt University, Jambo Drive, Riverside, Kitwe, Kitwe, Zambia 2 School of Built Environment, Copperbelt University, Jambo Drive, Riverside, Kitwe, Kitwe, Zambia Article published on February 18, 2018 Key words: REDD+, Forests, Forest governance, Joint forest management, Greenhouse gas emissions Abstract To draw lessons for informing strategies for reducing emissions from deforestation and forest degradation and fostering conservation, sustainable management of forests and enhancement of forest carbon stocks (REDD+), this study assessed community members’ perceptions of the quality of forest governance in the joint forest management program relative to the ideal forest governance quality using the Katanino Joint Forest Management study area in Zambia. The study focused on six elements of good governance, namely participation, transparency, accountability, equity, efficiency and effectiveness. Using a two stage sampling procedure, data for this study was collected using questionnaires administered to 120 randomly selected community members who participated in the Joint Forest Management program in Serenje, Biwa and Bwengo villages of Katanino Joint Forest Management pilot area. Results showed considerable gaps between ideal quality of forest governance and the perceived quality of forest governance. One sample t-test results showed that the perceived quality of all the six governance elements were statistically different from the ideal quality of forest governance at the 95 % confidence interval, participation (t (119) = -76, ρ < 0.05), transparency (t (119) = -130, ρ < 0.05), accountability (t (119) = -82, ρ < 0.05), equity (t (119) = -53.47, ρ < 0.05), effectiveness (t (119) = -60, ρ < 0.05), efficiency (t (119) = -87, ρ < 0.05). Implications of these findings are highlighted through a governance lens to inform strategies for REDD+ implementation. *Corresponding Author: Jane Musole Kwenye  jane.kwenye@yahoo.com Journal of Biodiversity and Environmental Sciences (JBES) ISSN: 2220-6663 (Print) 2222-3045 (Online) Vol. 12, No. 2, p. 1-10, 2018 http://www.innspub.net
  • 2. J. Bio. Env. Sci. 2018 2 | Kwenye and Mwango Introduction Reducing emissions from deforestation and forest degradation and fostering conservation, sustainable management of forests and enhancement of forest carbon stocks (REDD+) has emerged as a key international strategy to halt land-use related emissions in developing countries (Corbera and Schroeder, 2011; Leventon et al., 2014; Matakala, 2016). A central tenet of the REDD+ mechanism involves performance-based payments that incentivize reductions in greenhouse gas (GHG) emissions from deforestation and forest degradation (Sekeleti, 2011). It is envisaged that well-designed REDD+ mechanisms will have positive effects on biodiversity, ecosystem conservation and the livelihoods of forest-dependent communities (Broekhoven et al., 2012; Kokwe, 2012). While REDD+ is intended to prevent forest loss (Leventon et al., 2014) and is not primarily a governance reform per se, it is argued that it will affect or could be affected by existing forest governance to a considerable extent (Iqbal and Hussain, 2013; Larson and Petkova, 2011).Moreover, in the recent past, the ‘writings’ on REDD+ mostly stress the need to focus on governance issues (Gregersen et al., 2010; Cobera and Schroeder, 2011) given that increasing the quality of governance tends to be associated with a decrease in deforestation rates and long-term carbon storage globally (Umemiya et al., 2010).Thus, to draw lessons for informing strategies for REDD+ implementation, this study assessed community members’ perceptions of the quality of forest governance in the joint forest management program relative to the ideal forest governance quality using the Katanino Joint Forest Management study area in Zambia. The Republic of Zambia is one of the developing countries piloting the UN-REDD programme, which is aimed at preparing countries for REDD+ implementation by building institutional and technical capacity (Matakala, 2016). As part Zambia's participation in the UN-REDD programme (Leventon et al., 2014), Joint Forest Management (JFM) has been identified as a forest management approach for implementing REDD+ (UNDP et al., 201; Kokwe, 2012). JFM is a forest management strategy under which the government represented by the Forestry Department and the local communities living adjacent to the local forests enter into an agreement to jointly protect and manage forests while sharing responsibilities and benefits (Kokwe, 2012; Matakala, 2016). The JFM approach enables local communities, by virtue of their rights over land, to invest in and derive benefits from the sustainable management and utilization of forest resources in their area (Mbewe, 2007). Forest governance arrangements that determined how central questions regarding forests, livelihoods and sustainability have been answered to date will also determine how they will be answered under REDD+ (Larson and Petkova, 2011). Thus, lessons and experiences from previous forest-related initiatives explored through a governance lens (Kanowski et al., 2011) are critical for informing strategies for REDD+ implementation. Identifying governance gaps (Pedroni et al., 2009) in previous forest-related initiatives in ways that are consistent with the principles of good forest governance is essential for REDD+ success (Kanowski et al., 2011). However, comprehensive studies focused on drawing lessons and experiences from JFM to inform strategies for REDD+ initiatives through a governance lens are rare in Zambia. Therefore, to address this gap, this study was aimed at assessing perceptions of the quality of forest governance in the joint forest management program relative to the ideal forest governance quality using the Katanino Joint Forest Management pilot area in view of informing strategies for REDD+ implementation. The study focused on six elements of good governance namely participation, transparency, accountability, equity, efficiency and effectiveness. This is because good forest governance is associated with structures and processes that ensure multi-stakeholder participation, accountability of actors and decision makers, transparency of decision- making, efficient and effective management of forest resources, as well as fair and equitable allocation of resources and benefits (Larson and Petkova, 2011; Sekeleti, 2011).
  • 3. J. Bio. Env. Sci. 2018 3 | Kwenye and Mwango Material and methods Study site The Katanino JFM pilot area lies 80 km from Ndola and is traversed by the Ndola-Kapiri Road, the main highway that links Copperbelt Province to Lusaka, the nation's capital. Situated in Masaiti District in the Copperbelt Province of Zambia, Katanino JFM pilot area constituted one of the seven JFM pilot sites under the Provincial Forestry Action Programme (kokwe, 2012; Matakala, 2016). Villages situated in close proximity to Katanino Local Forest, with a population size of 3,842, were organized into four zones for purposes of JFM piloting. Katanino JFM area was chosen as a case study because it represents a hotspot endowed with richness of complex data ideal for governance exploration critical for informing strategies for REDD+ implementation. Notwithstanding the restriction of generalizing the findings of this study to other JFM areas, results of this highlight the governance issues that need to be considered in each context. Research instrument The questionnaire used in this study contained indicators reflecting elements of good governance (FAO &PROFOR, 2011). The elements included accountability, effectiveness, efficiency, equity, participation and transparency. These elements were chosen because they are comprehensive in nature and have a global relevancy (Iqbal and Hussain, 2013). Each element was measured using six indicators which represented differing facets of the elements to obtain a more well-rounded perspective of the elements (Hair et al., 2010).Modified to suit the local context, the indicators were adopted from Giri (2006), Gyawali (2009) and Iqbal and Hussain (2013). The indicators were scaled on a four-point Likert scale, 1 to 4 in an increasing order of poor, medium, good and excellent forest governance quality. Score 4 on the scale represented the ideal forest governance level. The questionnaire was pretested on 15 community members who participated in the JFM program in Serenje, Biwa, and Bwengo Villages in April 2017. Reliability assessment results showed that the indicators used to measure perceptions of participation, transparency, accountability, equity, effectiveness and efficiency had acceptable internal consistency with Cronbach's alpha ranging from 0.8 to 0.85. All items in the questionnaire were retained although some items were slightly modified in wording to improve comprehensiveness based on feedback from the pretest. Sampling design and sample size A two-stage sampling procedure was used in this study. In the first stage, three of the four villages organized during piloting the JFM program were randomly selected given that organization of the four villages was done arbitrarily (Umar and Vedeld, 2012). In the second stage, participants from three villages who participated in the JFM program were selected using simple random sampling. The minimum sample size for this study was determined using the confidence interval approach (Burns and Bush, 1995; Kwenye and Freimund, 2016). To obtain a 90% desired accuracy at the 90% confidence level with the response and usable rates set at 70 % and 10 % respectively, the required minimum sample size was 110. A total of 120 community members who participated in the Katanino JFM program were randomly selected in Biwa, Bwengo and Serenje villages. Data for this study was collected in April and May 2017. Data analysis Data for this study was analyzed using STATA 13.0 and Excel. Gap analysis, One-sample t-test and analysis of variance (ANOVA) at a significance level of ρ ≤ 0.05 were used to analyze the survey data. One sample t-test was conducted to determine whether the perceived quality for each of the six elements of forest governance were statistically different from the ideal quality of forest governance. Consequently, the mean score for each of the six elements of forest governance were compared with the mean score of 4 and six null hypotheses were tested: (i) H0: actual mean scores of participation = ideal mean score of 4,
  • 4. J. Bio. Env. Sci. 2018 4 | Kwenye and Mwango (ii) H0: actual mean scores of transparency = ideal mean score of 4, (iii) H0: actual mean scores of accountability = ideal mean score of 4, (iv) H0: actual mean scores of equity = ideal mean score of 4, (v) H0: actual mean scores of effectiveness = ideal mean score of 4, and (vi) H0: actual mean scores of efficiency = ideal mean score of 4. The one way ANOVA was conducted to determine if there were statistically significant differences in the mean of respondents' scores (i.e. actual mean scores) for participation, transparency, accountability, equity, effectiveness and efficiency based on the three villages - Serenje, Biwa and Bwengo. Gap analysis between respondents’ scores on the quality of forest governance and the score for the ideal quality of forest governance was undertaken using the spider chart, mean scores and percentages. Outliers and distribution of all measured variables were examined to purify the data and reduce systematic errors. Normality assessment results showed that the data did not deviate from multivariate normality. Outlier detection results showed that there were no outliers in the data. Results and discussion Demographic characteristics of study sample General demographic characteristics of the study sample are provided in Table 1. Table 1. General demographic characteristics of study sample. Characteristic Percentage Sex Female 60.0 Male 40.0 Age 40-45 37.5 46-55 38.3 56-65 22.5 > 66 1.7 Annual household income < K10,000 75.0 K10,000 - K20,000 25.0 Education level Primary 57.0 Secondary 43.0 An analysis of the study sample shows that males were in the majority (60 %) with the most represented age group being 46-55 years old (38%). The results also showed that majority of the respondents earned less than K10, 000 annually (75 %). Summary statistics of respondents’ perception of the quality of forest governance Summary statistics for respondents’ perceptions of the quality of the six forest governance elements are provided in Table 2.Participation had the highest mean score of 2.79, while equity had the lowest mean score of 2.01.
  • 5. J. Bio. Env. Sci. 2018 5 | Kwenye and Mwango Table 2. Summary statistics for the governance elements. Forest governance element Mean SD Participation 2.79 0.17 Transparency 2.31 0.14 Accountability 2.02 0.23 Effectiveness 2.44 0.28 Equity 2.01 0.41 Efficiency 2.42 0.20 A comparison of respondents’ mean scores and the ideal score of 4 representing good forest governance showed that respondents’ mean scores for all the six elements of forest governance were below the ideal score (Table 3). Table 3. Comparison of ideal and actual quality of forest governance elements: Achievement and gap analysis. Elements of Forest Governance Mean score (Ideal) Mean score (Actual) Achievement (%) Gap (%) Participation 4 2.79 69.75 30.25 Transparency 4 2.31 57.75 42.25 Accountability 4 2.02 50.50 49.50 Equity 4 2.01 50.25 49.75 Effectiveness 4 2.44 61.00 39.00 Efficiency 4 2.42 60.50 39.50 Comparison of actual and ideal forest governance by achievement and gap analysis Gap analysis results showed that respondents’ actual scores for equity had the largest variance from the ideal score for good forest governance (49.6%) while participation had the smallest variance (30.3%). In terms of closeness to the ideal standard for good forest governance, the achievement analysis results showed that participation had the highest achievement (69.8%) while equity had the lowest achievement (50.3%). Table 4. Mean score and a comparison of ideal and actual quality of forest governance elements in Serenje, Biwa and Bwengo villages: Gap analysis. Elements of Forest Governance Serenje Village Biwa Village Bwengo Village Mean score (Actual) Mean score (Ideal) Gap (%) Mean score (Actual) Mean score (Ideal) Gap (%) Mean score (Actual) Mean score (Ideal) Gap (%) Participation 2.79 4 30.3 2.79 4 30.3 2.78 4 30.5 Transparency 2.33 4 41.8 2.31 4 42.3 2.31 4 42.3 Accountability 2.04 4 49.0 2.03 4 49.3 1.99 4 50.3 Equity 2.02 4 49.5 1.98 4 49.5 2.04 4 49.0 Effectiveness 2.45 4 38.8 2.42 4 39.5 2.45 4 38.8 Efficiency 2.42 4 39.5 2.44 4 39.0 2.41 4 39.8 This is finding is consistent with the spider web chart results in Figure 1 which showed that respondents’ mean score for participation had the smallest gap from the ideal score for good forest governance while equity had the largest gap. Similarly, as shown in Table 4, gap analysis results for Serenje, Biwa and Bwengo villages showed that the respondents’ mean scores for each of the six elements of good forest
  • 6. J. Bio. Env. Sci. 2018 6 | Kwenye and Mwango governance were below the ideal score of 4. Additionally, for all the three villages, results showed that participation had the smallest variance from the ideal score for good forest governance. Overall, an analysis of respondents’ mean scores and the gap analysis results showed that respondents perceived good forest governance to have been reflected more through participation, effectiveness and efficiency than through equity, accountability and transparency. This finding is in contrast with Iqbal and Hussain (2013) whose results showed that good forest governance was reflected more through transparency and equity than through participation and effectiveness using a Pakistan setting. Table 5. ANOVA results for statistical differences between groups: Serenje, Biwa and Bwengo villages. Element Source DF SS MS F ρ Participation Between groups 0.005 2 0.003 0.09 0.914 Within groups 3.603 117 0.031 Total 3.609 Transparency Between groups 0.014 2 0.007 0.36 0.697 Within groups 2.319 117 0.020 Total 2.333 Accountability Between groups 0.054 2 0.027 0.49 0.612 Within groups 6.421 117 0.054 Total 6.475 Effectiveness Between groups 0.020 2 0.010 0.12 0.886 Within groups 9.563 117 0.082 Total 9.583 Equity Between groups 0.060 2 0.030 0.18 0.838 Within groups 19.672 117 0.168 Total 19.731 Efficiency Between groups 0.018 2 0.009 0.23 0.795 Within groups 4.591 117 0.039 Total 4.609 Comparison of respondents’ perceptions of the quality of forest governance across the three villages Table 5 showed that for all the six elements there were no statistical differences between respondents’ perceptions of the quality of forest governance in the three villages namely Biwa, Serenje and Bwengo at the 95 % confidence interval. Thus, it has been demonstrated that perceptions of respondents were consistent across the villages. Results of this study are in line with Iqbal and Hussain (2013) who also reported consistence of the perceptions of their respondents using a Pakistan setting. Comparison of actual and ideal quality of forest governance Table 6 showed results of the comparison of the mean ideal score and the mean scores for each of the six elements of forest governance. The results showed that respondents’ mean scores for the six elements were statistically different from the ideal mean score of 4 at the 95 % confidence interval. Therefore, all the six null hypotheses tested in this study are rejected. Rejection of the null hypotheses has demonstrated that the perceived quality of each of the six elements of forest governance differed from the ideal quality of each of these elements.
  • 7. J. Bio. Env. Sci. 2018 7 | Kwenye and Mwango Lessons for REDD+ implementation in Zambia Empirical evidence in this study has shown that respondents perceived the quality of forest governance in the JFM program to be lower than the ideal quality of good forest governance. That is, all the six elements of good forest governance were perceived to be lower than the ideal quality of good forest governance. Consequently, this study’s finding provides lessons for REDD+ implementation in Zambia. Specifically, it reveals the need for forest governance reforms when employing the JFM model, in particular around mechanisms for equitable decision making processes, as well as mechanisms for fostering and strengthening transparent and accountable institutions and decision making processes. Forest governance reforms tailored to addressing equity require ensuring that all the stakeholders, particularly the most vulnerable have the opportunity to participate in the decision making process. Moreover, their interests need to be considered by decision makers in the decision making process. Table 6. One sample t-test results. Element Mean SD t-value DF ρ Participation 2.79 0.17 -76.27 119 0.000 Transparency 2.32 0.14 -130 119 0.000 Accountability 2.02 0.23 -91.94 119 0.000 Equity 2.01 0.41 -53.47 119 0.000 Effectiveness 2.44 0.28 -60.10 119 0.000 Efficiency 2.42 0.20 -87.89 119 0.000 With regards to accountability, reforms should be tailored to establishing mechanisms that ensure that institutions with decision making authority have an obligation to report, explain and be answerable for the consequences of decisions they make. Such mechanisms include, for example, establishing clear criteria for evaluating the performance of decision makers. Furthermore, establishing internal and external audits to provide checks and balances is critical for fostering accountability. Linked with accountability is the issue of transparency (DESA, 2009). Transparency in decision making is considered as an important factor in improving the ability of stakeholders to hold key decision makers accountable for their actions (Broekhoven et al., 2012). Moreover, it helps to build trust between stakeholders and break down barriers between historically opposed parties (Sekeleti, 2011). Results of this study have shown that if the JFM model is to be used to implement REDD+ strategies, there is need to ensure that stakeholders, particularly the local communities follow and understand the decision making process. This requires involving them at every stage of the decision making process. Further, clarity on how and why decisions are made is fundamental for fostering transparency. This requires ensuring that information on decisions and the decision making processes are available and accessible by all the stakeholders (DESA, 2009). Safeguards intended to ensure that REDD+ delivers win-win scenarios whereby forests are conserved alongside community development (Harvey et al., 2010; Kelly, 2010) include requirements for full and effective participation of relevant stakeholders including local communities (UNFCCC, 2010). A critical aspect that fosters participation is the involvement of multi-stakeholders in the decision making process. Therefore, if JFM is to be used as a model for delivering REDD+ with safeguards, greater attention must be paid to strengthening multi- stakeholder participation. This necessitates the need to avoid peripheral involvement of sectors that influence forest management such as agriculture and energy among others.
  • 8. J. Bio. Env. Sci. 2018 8 | Kwenye and Mwango Enhanced intersect oral collaboration linked to village and forest area management governance structures is fundamental in view of considering REDD+ within the wider livelihood activities of forest communities (Leventon et al., 2014). Such an endeavor requires developing sustained structures for intersect oral collaboration. Intersect oral collaboration is fundamental in ensuring that REDD+ creates incentives that ensure lasting and achievable emission reductions while maintaining and improving other ecosystem services that forest provide (Sekeleti, 2011). Forest governance reforms will need to be complemented by reforms across sectors that affect forests. This is because policies outside the forestry sector have a significant impact on forests (Broekhoven et al., 2012; Sekeleti, 2011). Furthermore, the governance reforms will need to be supported by implementation actions at the village level in order for REDD+ to be an opportunity for delivering community benefits (Leventon et al., 2014). Moreover, designing transparent financial structures for the performance-based implementation of the REDD+ strategy that allows for an equitable distribution of benefits is critical. Additionally, understanding the community context and the way that the design of REDD+ initiatives fits to this context as well as the role of the broader policy context in shaping support for JFM operations is fundamental. Fig. 1. Comparison between actual and ideal scores for six elements of good forest governance. Implementing the elements of good forest governance needs to begin with defining priorities as well as a sequence for Zambia to develop the capacity of stakeholders to administer the components of good governance. Furthermore, a strategic and practical approach to improving governance should be dynamic and responsive to emerging topics and interests (Broekhoven et al., 2012). In this regard, what may be considered as the focus of governance reforms currently should not be considered 'good enough’ a number of years from now. Rather, it should be viewed as part of a planning process on how to move forward and build on achievements. In addition, there is need to promote forest governance monitoring which will aid in making changes that respond to new priorities, address new weaknesses and build on new strengths.
  • 9. J. Bio. Env. Sci. 2018 9 | Kwenye and Mwango Conclusion This study has shown considerable gaps between the ideal quality of forest governance and the perceived quality of forest governance. Among the six elements of forest governance, equity had the largest variance from the ideal quality of forest governance (49.6%) followed by accountability (49.5%) and transparency (42.3%) with participation had the smallest variance (30.3%). Achievement analysis showed that participation had the highest achievement (69.8%) followed by effectiveness (61%) and efficiency (60.5%) with equity had the lowest achievement (50.3%). For all the six elements there were no statistical differences between the perceptions of respondents in the three villages namely Biwa, Serenje and Bwengo at the 95 % confidence interval, participation (F(2,117) = 0.09, p = .913), transparency (F(2,117) = 0.36, p = 0.697) , accountability (F(2,117) = 0.49, p = 0.612), equity (F(2,117) = 0.18, p = 0.838), effectiveness (F(2,117) = 0.12, p = 0.886) and efficiency (F(2,117) = 0.23, p = .795). Thus, the study has shown that respondents' perceptions of the quality of forest governance as reflected by participation, transparency, accountability, equity, effectiveness and efficiency were consistent across the three villages. The perceived quality of all the six governance elements were statistically different from the ideal quality of forest governance at the 95 % confidence interval, participation (t (119) = -76, ρ < 0.05), transparency (t (119) = -130, ρ < 0.05), accountability (t (119) = -82, ρ < 0.05), equity (t (119) = -53.47, ρ < 0.05), effectiveness (t (119) = -60, ρ < 0.05), and efficiency (t (119) = -87, ρ < 0.05).Therefore, the study has shown that the perceived quality of each of the six elements of forest governance differed from the ideal quality of each of these elements. References Broekhoven G, Savenije H, Scheliha S. 2012. Moving forward with forest governance. European Tropical Forest Network News. Issue No. 53. Burns AC, Bush RF. 1995. Marketing research. New Jersey: Prentice Hall. Corbera E, Schroeder H. 2011. Governing and implementing REDD+. Environmental Science and Policy 14, 89-99; http://dx.doi.org/10.1016/j.envsci.2010.11.002. DESA. 2009. Public governance indicators: A literature review. United Nations. New York. FAO, PROFOR. 2011. Assessing and monitoring forest governance: A user's guide to a diagnostic tool. Programme on Forests. GFI. 2009. The governance of forest toolkit (version 1): A draft framework of indicators for assessing governance of the forest sector. The governance of forests initiative. Giri K. 2006. Resource complexities and governance mechanisms: Evaluating community forestry program of Nepal. University of Natural Resources and Applied Life Sciences. Austria. Gregersen H, El Lakany H, Karsenty A, White A. 2010. Does the opportunity cost approach indicate the real cost of REDD+. Rights and Realities of paying for REDD+. Rights and Resources Initiative. Washington DC. Gyawali A. 2009. Assessing governance of community forest user groups: A case study from Makwanpur District, Nepal. B.Sc. Forestry research thesis. Tribhuvan University. Institute of Forestry. Pokhara Nepal. Harvey CA, Dickson B, Kormo C. 2010. Opportunities for achieving biodiversity conservation through REDD. Conservation Letters 3(1), 53-61. http://dx.doi.org/10.1111/j.1755-263x.2009.00086.x Kanowski PJ, McDermott CL, Cashore BW. 2011. Implementing REDD+: Lessons from analysis of forest governance. Environmental Science and Policy 14(2), 111-117. http://doi.org/10.1016/j.envsci.2010.11.007
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