Understory Flora Composition Assessment of Jabonga, Agusan del Norte
1. UNDERSTORY FLORA COMPOSITION ASSESSMENT
OF JABONGA, AGUSAN DEL NORTE
JONI REY H. CAMPILAN
An Undergraduate Thesis
Submitted to the Science Department
College of Natural Science and Mathematics
Mindanao State University
Fatima, General Santos City
In Partial Fulfillment of the Requirements
for the Degree
BACHELOR OF SCIENCE IN BIOLOGY
MARCH 2013
2. APPROVAL SHEET
This undergraduate thesis entitled ―UNDERSTORY FLORA COMPOSITION
ASSESSMENT OF JABONGA, AGUSAN DEL NORTE‖, prepared and submitted
by JONI REY H. CAMPILAN, in partial fulfillment of the requirements for the
Degree of Bachelor of Science in Biology, has been examined and approved.
THESIS COMMITTEE
______________________________
JAIME NAMOCATCAT, Ph.D.
Adviser
__________________________ _______________________
PROF. CARMEN R. NISPEROS FLORENCE L. ZAPICO, MS
Member Member
________________________________________________________________
This undergraduate thesis is hereby officially accepted in partial fulfillment of the
requirements for the degree Bachelor of Science in Biology.
__________________________ ____________________________
PROF. CARMEN R. NISPEROS MA. LOURDES dM. GALIA, Ph.D
Chairperson Dean
______________________ ______________________
Date Date
ii
3. PERSONAL DATA
The researcher was born in Tboli Evangelical Clinic and Hospital, Inc. on
January 6, 1993. He is the eldest of the two sons of Ptr. Nicolas P. Campilan and
Mrs. Joan H. Campilan.
When he was four years old, he took his preschool education at TLDFI
(Tribal Leaders Development Foundation, Inc.) Learning Center where he finished
as second honors. His primary education was completed at Lugan Central
Elementary School where he graduated as first honors. He pursued his secondary
education at Edwards National High School and graduated as the class
valedictorian.
With great dedication in the field of science, he took the degree BS Biology
at Mindanao State University-General Santos City. His learning experiences
taught him that life is not perfect but it was very good, time is never lasting, and
relationship must be prioritized than any other things.
Now as he continue to delight himself in the Lord let it be that the desires of
his heart will be fulfilled.
JONI REY H. CAMPILAN
iii
4. ACKNOWLEDGEMENT
This study will not be accomplished without our Almighty God who brought
all possibilities in the life of the researcher and the completion of this paper. To
God be the glory and honor!
The researcher would like to express his great gratitude to his family for the
love, support and encouragement they had shown; to his mother who teaches him
how to sacrifice, to his father who taught me him how to trust God and to his
brother who taught him how to care for others.
To his adviser, Dr. Jaime Namocatcat, who taught him to excel in all things.
To Dr. Apolinario Remollo, who never ceases to share his knowledge. And to his
team mates, Victoria Mijares, Dwight Invidiado, Angelie Abistano, Joan De Asis,
and to the two guides who strengthen him in his study. To Ms Catherine Aguilar,
who took care of him during the field work, and to the people of Jabonga, Agusan
del Norte who inspire him to pursue this study.
To his friends Vanessa Bidad, Paolo Tagaloguin, Adrian Peñaflorida, Anne
Tarazona, Ressy Mae Ruelan, Ruth Jean Maratas, and Cherry Mae Labrador. To
his ‗Nanays‘, Dory Magabullo and Jane Villarosa. To my SRM family- Tay Dodz,
Steph, Dave, Benj, Bem, Bea, Joy, Love, Jonivee, & Jebee. Thank you for
bringing joy in his life.
Not only that I was knit together in my mother’s womb, I was on the right
place with the right people on the right time.
JONI REY H. CAMPILAN
iv
5. TABLE OF CONTENTS
APPROVAL SHEET........................................................................................................ ii
PERSONAL DATA..........................................................................................................iii
ABSTRACT…………………………………..……………………………………………….….ix
1. INTRODUCTION........................................................................................................... 1
1.1 Objectives of the Study .................................................................................. 2
1.2 Significance of the Study ............................................................................... 2
1.3 Scope and Limitation ...................................................................................... 3
2. REVIEW OF RELATED LITERATURE ............................................................. 4
2.1 Philippine Biological Diversity ....................................................................... 4
2.1.1 Philippine Biodiversity Conservation and Management Strategies ............ 4
2.2. Understanding Understory Vegetation Diversity .......................................... 6
2.2.1 Effects of Disturbances to Understory Vegetation Diversity ....................... 7
2.3 Belt Transect Sampling Method ..................................................................... 8
2.4 Sampling Parameters ....................................................................................10
3. MATERIALS AND METHODS .........................................................................12
3.1 Description of Study Site...............................................................................12
3.2 Sampling Method ...........................................................................................14
3.2.1 Sampling Materials ........................................................................................15
3.2.2 Species Processing and Identification .........................................................15
3.3 Data Analysis .................................................................................................16
4. RESULTS AND DISCUSSION ........................................................................19
4.1 Species Composition and Richness .............................................................19
4.2 Ecological Measurement ...............................................................................21
4.2.1 Dinarawan, San Pablo, Jabonga ...................................................................21
4.2.1.1 Transect 1 .......................................................................................................21
4.2.1.2 Transect 2 .......................................................................................................23
4.2.1.3 Transect 3 .......................................................................................................26
4.2.1.4 Transect 4 .......................................................................................................27
4.2.2 Kabugaw, San Pablo, Jabonga .....................................................................29
4.2.2.1 Transect 5 .......................................................................................................29
4.2.2.2 Transect 6 .......................................................................................................31
v
6. 4.2.3 Uba, San Pablo, Jabonga ..............................................................................33
4.2.3.1 Transect 7 .......................................................................................................33
4.2.3.2 Transect 8 .......................................................................................................35
4.2.3.3 Transect 9 .......................................................................................................37
4.2.4 Magdagooc, Jabonga ....................................................................................39
4.2.4.1 Transect 10 .....................................................................................................39
4.2.4.2 Transect 11 .....................................................................................................41
4.3 Diversity Index ...............................................................................................43
4.4 Assessment of Conservation Status ............................................................44
5. SUMMARY, CONCLUSION, AND RECOMMENDATIONS .............................51
LITERATURE CITED .....................................................................................................55
APPENDIX 1. Understory Flora Assemblage Transects and Quadrats
in Jabonga, Agusan del Norte ..........................................................66
APPENDIX 2. Transect Coordinates .......................................................................65
APPENDIX 3. Study Sites and Transect Lines .......................................................76
APPENDIX 3. Understory Flora Sampling ..............................................................80
APPENDIX 4. Species List of Understory Flora In Jabonga, Agusan Del Norte ..81
APPENDIX 5. DENR Assessment of Conservation Status
of Threatened Plant Species (DAO 2007-1) .....................................95
APPENDIX 6. Guingab (1994) Assessment of Floral Species
Conservation Status .........................................................................98
APPENDIX 7. Ecological Measurements of Understory Flora Species In Jabonga,
Agusan Del Norte ..............................................................................99
APPENDIX 8. Photographs of Understory Flora in Jabonga…………...…………130
vi
7. LIST OF TABLES
Table 1. Ecological Measurements for Transect 1 in Dinarawan, Jabonga 21
Table 2. Ecological Measurements for Transect 2 in Dinarawan, Jabonga 23
Table 3. Ecological Measurements for Transect 3 in Dinarawan, Jabonga 25
Table 4. Ecological Measurements for Transect 4 in Dinarawan, Jabonga 27
Table 5. Ecological Measurements for Transect 5 in Kabugaw, Jabonga 29
Table 6. Ecological Measurements for Transect 6 in Kabugaw, Jabonga 31
Table 7. Ecological Measurements for Transect 7 in Uba, Jabonga 32
Table 8. Ecological Measurements for Transect 8 in Uba, Jabonga 34
Table 9. Ecological Measurements for Transect 9 in Uba, Jabonga 37
Table 10. Ecological Measurements for Transect 10 in Magdagooc, Jabonga 39
Table 11. Ecological Measurements for Transect 11 in Magdagooc, Jabonga 41
Table 12. Conservation Status of Understory Flora Based on Guingab (1994) 48
vii
8. LIST OF FIGURES
11
Figure 1. Map of Jabonga, Agusan del Norte, N 090 07' 14.6" E 1250 31' 50.9"
Figure 2. Schematic flowchart of study, indicators, method, and metrics for 17
assessment of the understory flora composition, and conservation status
18
Figure 3. Total No. of Species in Understory Flora Assessment in Jabonga
22
Figure 4. Transect 1 Cumulative Species-Area Curve, Dinarawan, Jabonga
29
Figure 5. Transect 2 Cumulative Species-Area Curve, Dinarawan, Jabonga
26
Figure 6. Transect 3 Cumulative Species-Area Curve, Dinarawan, Jabonga
28
Figure 7. Transect 4 Cumulative Species-Area Curve, Dinarawan, Jabonga
30
Figure 8. Transect 5 Cumulative Species-Area Curve, Kabugaw, Jabonga
31
Figure 9. Transect 6 Cumulative Species-Area Curve, Kabugaw, Jabonga
33
Figure 10. Transect 7 Cumulative Species-Area Curve, Uba, Jabonga
35
Figure 11. Transect 8 Cumulative Species-Area Curve, Uba, Jabonga
38
Figure 12. Transect 9 Cumulative Species-Area Curve, Uba, Jabonga
40
Figure 13. Transect 10 Cumulative Species-Area Curve, Magdagooc, Jabonga
Figure 14. Transect 11 Cumulative Species-Area Curve, Magdagooc, Jabonga 42
Figure 15. Simpson's Diversity Index of Understory Flora Vegetation in Jabonga 43
viii
9. ABSTRACT
CAMPILAN, JONI REY H. ―UNDERSTORY FLORA COMPOSITION
ASSESSMENT OF JABONGA, AGUSAN DEL NORTE‖. Undergraduate Thesis,
Mindanao State University, General Santos City
Thesis Adviser: DR. JAIME NAMOCATCAT
Understory flora of Jabonga, Agusan del Norte were assessed from May
13-18, 2012 using belt transect method in 11 transects measuring 4, 300 m in
length. 276 species of plants were collected resolved into 95 families and two
hundred ten (210) genera where 9 species are Aroids, 1 Bromeliad, 2 Fern Allies,
12 Ferns, 19 Grasses, 42 Herbs, 2 Orchids, 4 Palms, 90 Saplings, 4 Sedges, 32
Shrubs, 50 Vines, 1 Weed, and 4 Zingibers. Euphorbiaceae (18 spp.) and
Moraceae (17spp.) family were highly represented under 4 and 14 genera,
respectively. Simpson‘s Diversity Index Value was calculated highest at 0.963 for
Transect 1 and lowest at 0.871 for Transect 4, suggesting moderate to high
diversity. Based on DAO 2007-01, Pterocarpus indicus Willd. Forma indicus
(Smooth Narra) is listed as Critically Endangered; Afzelia rhomboidea (Blanco)
Vidal (Tindalo) is endangered; Alangium longiflorum Merr. (Malatapay),
Cynometra inaequefolia A. Gray (Dila-dila), Dillenia reifferscheidia Naves
(Katmon Kalabaw), Mangifera merrillii (Pahong Liitan), Securinega flexousa
(Muell,-Arg.) (Anislag), Shorea contorta (White Lawaan), and Vitex parviflora
Juss. (Molave) are vulnerable, and Aglaia luzoniensis (Kuling manok) and Dillenia
philippinensis Rolfe (Katmon Baging) are other wildlife species. The presence of
Nephrolepsis biserrata (Sw.) Schott (Pakong Kalabaw), the most abundant
species, Chromolaena odorata (Hagonoy) and Saccharum spontaneum L.,
(Talahib), invasive species, which considered to have dense population, might
have cause biodiversity loss. With this threats to the biodiversity of the area and
with the observed exploitation activities, the area is considered to be at high risk.
The study reveals the utmost need of Jabonga for biodiversity conservation
strategies.
ix
10. 1. INTRODUCTION
As one of the world‘s eight biodiversity hottest hotspots (Myers et al,
2000), the Philippines is home to some of the most endangered habitats and
species in the world. Due to the extraordinary rate of environmental destruction,
leaving only 3% of the land with primary forest, this biodiversity is at high risk.
Despite that situation, information on Philippine forest vegetation is fragmentary
and focused on trees (Langerberger et al., 2006). Forest management to
diversify tree species is now being promoted to favor biodiversity (Barbier et al.,
2008).
Understory vegetation is influenced by overstory composition and
structure through modifications of resource availability (light, water and soil
nutrients) and other effects, such as physical characteristics of the litter layer
(Barbier et al., 2008). Vegetation has been widely used to describe habitat
characteristics, water quality and make predictions about the presence and
composition of the surrounding communities (Appelgren and Mattila, 2005). The
composition of understory is usually different from that of the canopy, and thus
supports a different fauna than does the canopy (Gentry and Emmons, 1987).
The physical structure of the understory plants provides food resources for many
species of insects, birds, and mammals, and is responsible for a high percentage
of total diversity in the tropical forests (Tchouto et al., 2006).
1
11. Composition of the vegetative community as well as diversity must be
examined in order to accurately assess differences among communities and the
possible effects of disturbance, including human induced disturbance.
This study investigated the understory flora composition of the remnant
seconcary forests of Jabonga, Agusan del Norte. Conservation status
assessment of plants in the study site was done in order to evaluate the area‘s
biodiversity.
1.1 Objectives of the Study
This study sought to:
1. Collect, classify, and identify understory plants of Jabonga, Agusan del
Norte.
2. Assess the composition and distribution of the identified specimen in
terms of Density, Relative Density, Frequency, Relative Frequency,
Dominance, Relative Dominance, Species Diversity, and evenness.
3. Evaluate the conservation status of plants documented based on DAO
2007-01 and IUCN (International Union for the Conservation of Nature)
Red List on plants.
1.2 Significance of the Study
Results of this study will serve as baseline information on species
richness, composition, distributional range, species‘ population size and
structure, and conservation status of understory plants inJabonga, Agusan del
2
12. Norte. The given information on the, endemic and endangered plant species will
assist evolving long term habitat conservation, species prioritization, and natural
resources management plan on the area. Furthermore, this will aid the
developing core objectives for the conservation monitoring and decision
makingof the area.
1.3 Scope and Limitation
Composition of understory plant flora was studied in Jabonga, Agusan del
Norte. This study was focused on the inventory and assessment of understory
flora of ≤ 3 m in height of the area. This includes all flora and grass species
including the seedlings, herbs, vines, rattans, saplings and other undergrowths.
Determination of the species composition was confined only on the established
transects along its trails and peripheries. Identification of the different collected
species was based on the directly observable and basic morphological features
of individual species with no extensive anatomical study made. At least, genus
level of documented plant species was identified. Density, relative density,
frequency, relative frequency, dominance, relative dominance, and species
diversity and evenness were the ecological parameters determining the
composition and distribution of understory flora of the area. Conservation status
assessment of understory plants was solely base on the sampled species, and
searched plants.
3
13. 2. REVIEW OF RELATED LITERATURE
2.1 Philippine Biological Diversity
The Philippines has vast natural resources that are source of food,
water, shelter and livelihood for its rapidly growing population. It is one of 17
megabiodiversity countries (containing 2/3 of the earth‘s biodiversity and about
70-80% of the world‘s plant and animal species) due to its geographical isolation,
diverse habitats and high rates of endemism (native, restricted or unique to a
certain country or area). The Philippines is 5th in the number of plant species and
maintains 5% of the world‘s flora (DENR, 2008).
The vegetation of the Philippines is very rich and diverse and a major
proportion of the country is covered with tropical forests. There are varieties of
vines, epiphytes, climbers. Flowering plants including ferns and orchids grow in
large number in the forests of the Philippines (Langenburger, 2004). Philippine
species endemism is very high, covering at least 25 genera of plants. The
Philippines is also one of the world‘s biodiversity hotspots, with a large number of
endangered and threatened species and habitats, making it one of the world‘s
top global conservation priority areas (DENR, 2008).
2.1.1 Philippine Biodiversity Conservation and Management Strategies
Biodiversity maintenance is a key management objective and a requisite
for sustainable forestry (Torras and Saura, 2008). Approaches with a
4
14. combination of both site-specific biodiversity measures and assessments of
habitat diversity and heterogeneity are not yet established, but in the near future
may lead to a scientifically based evaluation of the potential for increasing
biodiversity by appropriate landscape management (Duelli, 1997).
Philippines, a developing country, works with simple monitoring plan to
work out conservation and management of its biodiversity (Danielsen, et.al,
2000). Providing human resource, as major lacking power, is addressed with the
given strategies. Wherein, the monitoring system aims to identify trends in
biodiversity and its uses so as to guide management action; it also promotes the
participation of local people in the management, stimulates discussion among
stakeholders and builds the capacity of park staff and communities in
management skills. In addition, it seeks to provide people with direction regarding
the aims of protected areas, and reinforces the consolidation of existing
livelihoods through strengthening community-based resource management
systems. The system can be sustained using locally available resources. The
countries‘ approach is useful in where it embarks on shared management of park
resources with local communities, where rural people depend on use of natural
ecosystems, and where the economic resources for park management are
limited.
On forestry, the major strategy is the Community Based Forest
Management, CBFM (Lasco & Pulhin, 2006) CBFM focuses on forest and land
management and it includes management of tropical forests (enrichment
5
15. planting, timber stand improvement or TSI and limited harvesting), rehabilitation
of degraded lands [reforestation, assisted natural regeneration (ANR)] and
agroforestry. The action has positive results that led to conservation of natural
forests and the associated biodiversity. Tree planting in farms and landscapes
has led to soil and water conservation, carbon sequestration and biomass
production.
In small ways, zoos meet their conservation role through captive
breeding, education, research, animal-welfare, environmental enrichment,
reintroduction, and support for in situ conservation of species and their habitats
(Catibog-Sinha, 2008). Another is ecotourism that has been identified as one of
the measures to achieve biodiversity conservation at both in situ (e.g. protected
areas) and ex situ (e.g. zoos) conditions (Catibog-Sinha, 2010).
2.2. Understanding Understory Vegetation Diversity
The understory layer is a critical component of forest ecosystems typically
supporting the vast majority of total ecosystem floristic diversity (Halpern and
Spies, 1995; Gilliamand Roberts, 2003) and providing habitat elements to
associatedwildlife species (Carey and Johnson, 1995). These communities also
play a central role in the dynamics and functioning of forestecosystems by
influencing long-term successional patterns (Phillips and Murdy, 1985; Abrams
and Downs, 1990; Oliver andLarson, 1996; McCarthy et al., 2001; Royo and
Carson, 2005;Nyland et al., 2006) and contributing to forest nutrient
6
16. cycles(Chapin, 1983; Zak et al., 1990; Anderson and Eickmeier, 2000;Chastain
et al., 2006).
Understory vegetation is influenced by overstory composition and
structure through modifications of resource availability (light, water and soil
nutrients) and other effects, such as physical characteristics of the litter layer.
Overstory light transmittance and diverse properties of forest litter are factors that
have been most fully studied to date, but other factors such as throughfall water
quantity and chemistry may also play a role (Barbier et al., 2008). Understory
plant species assemblages may have different patterns of diversity than tree
species because of variable responses to different abiotic factors.
Forests growing on former agricultural land often have reduced
frequencies of many native forest herbs compared with forests that were never
cleared for agriculture. A leading explanation for this pattern is that many forest
herbs are dispersal limited, but environmental conditions may also hinder
colonization. It is suggested that some plants growing in post-agricultural stands
may be N (nitrogen) limited, whereas undisturbed stands in this region appear to
be approaching N saturation (Fraterrigo et al., 2009).
2.2.1 Effects of Disturbances to Understory Vegetation Diversity
An intermediate disturbance hypothesis states that diversity is highest at
intermediate disturbance levels. Stand improvement treatments increased the
7
17. number of large diameter trees, tree species richness and diversity (cleaning and
thinning), and shrub species richness (pruning) (Torras and Saura, 2008).
In a study, thinning and burning treatments are a common method of
reducing fire risk while simultaneously promoting understory production. These
ecological restoration treatments did promote a more diverse and abundant
understory community. The disturbances generated by these treatments also
promoted an invasion by an undesirable nonnative species (McGlone et
al.,2009).
2.3 Belt Transect Sampling Method
Numerous vegetation sampling techniques are outlinedin sampling
textbooks (Mueller-Dombois & Ellenberg1974; Krebs 1989; Kent & Coker 1994;
and Barbour et al.1999) and in the scientific literature (Stohlgren et al.
1995;Etchberger & Krausman 1997; Stohlgren et al. 1998) for quantifying
different plant community attributes.
Although there is no one correct technique for sampling vegetation, the
sampling design chosen may greatly influence the conclusions researchers can
draw from restoration treatments. Considerations when designing vegetation
sampling protocol include determining what sampling attributes to measure, the
size and shape of the sampling plot, the number of replicates and their location
within the study area, and the frequency of sampling (Korb et al., 2003).
Sampling methods to estimate total species richness of a defined area
8
18. (conservation unit, national park, field station, "community") will play an important
role in research on theglobal loss of biodiversity. Such methods should be fast,
because time is of the essence. They shouldbe reliable because diverse workers
will need to apply them in diverse areas to generate comparabledata. They
should also be simple and cheap, because the problem of extinction is most
severe indeveloping tropical countries where the scientific and museum
infrastructure is often still rudimentary (Coddington et al, undated).
Sutter (1996) outlined four criteria of monitoringtechniques that must be
met to reliably and precisely detect change: (1) Data need to have a known and
acceptable level of precision; (2) data sampling techniques needto be repeatable;
(3) data need to be collected for a longenough time to capture responses to
treatments; and (4) techniques need to be feasible, realistic, and inexpensive
enough to be maintained long term.
Determining the sampling technique that shouldbe used for a particular
study needs to take into consideration numerous factors such as the restoration
goals, sampling attributes, level of sampling precision, and financialand
personnel constraints (Korb et al., 2003). In this study two 1x1m Belt Transect
was spaced 10m apart across ends of 20m transect line. The primary objective of
the belt transect is to obtain a species list of the area (Kent& Coker 1994). All
herbaceous and shrub species within the belt were recorded including their
foliage cover data.
9
19. 2.4 Sampling Parameters
Species diversity is one of the most frequently sampled attributes in
vegetation studies (Ricklefs & Schluter 1993). Species diversity is often used
interchangeably with species richness.Species richness, however, is one of two
components thatdefine species diversity, the other being species evenness (Kent
& Coker 1994). The well-known concept states that an increase in sampling area
will increase species richness detection (Rapson et al. 1997).
Species abundance is some measure of the amount of a species in a
sample (Chiarucci et al. 1999). Plant community attributes that measure species
abundance include plant foliar cover, plant density, and plant frequency. Plant
foliar cover is one of the most widely used abundance measurements because it
is not biased by the size or distribution of individual species as plant density and
plant frequency measurements can be (Floyd & Anderson 1987). Ecologists have
designed numerous sampling techniques to quantify plant foliar cover. The three
most commonly used techniques include the point-intercept, the line-intercept,
and ocular estimation (Buckner 1985).
Visual estimation of plant cover is oneof the most common measurements
in plant ecology and restoration studies (Kennedy & Addison 1987). Ocular
estimates are normally taken within a 1m 2 area because one of the requirements
for accuracy is that observations must be made from a vertical perspective within
a bounded plot (Buckner 1985). Ocular estimates can either be estimated to the
nearest predetermined percent (e.g., closest 1%) or they can be categorized into
10
20. published cover classes (e.g., Daubenmire or Braun-Blanquet) (Mueller-Dombois
& Ellenberg 1974).
11
21. 3. MATERIALS AND METHODS
3.1 Description of Study Site
Agusan del Norte Province is located on wide, fertile, coastal plateau in
the northeastern part of Mindanao. This province is bordered on the north and
east by the Province of Surigao del Norte and Surigao del Sur, on the south by
the Province of Agusan del Sur, and on the southwest by the Province of
Misamis Oriental. Fertile, coastal plains and valleys along the Agusan River
characterize the terrain of Agusan del Norte Province. The average elevation is
46 meters above sea level: The climate is classified as tropical wet.
Temperatures of the coolest month are above 18°C, and rainfall in the driest
month is at least 60 mm.
Figure 1. Map of Jabonga, Agusan del Norte, N 090 07' 14.6" E 1250 31' 50.9"
12
22. There is a minimum of seasonal variation in temperature and precipitation, as
both remain high throughout the year. The province is large, 2,590 square
kilometers (Carney et al., 1978).
In Agusan del Norte, Lake Mainit is located where it is covered by
different vegetative groups: grassland, brush land, secondary forest , limestone
forest, marshland, riparian and lowland rice paddies. Municipality of Jabonga is
one of the Municipalities that surrounds Lake Mainit.
There are four study sites in Jabonga that are strategically selected for the
study of the understory flora namely Dinarawan, Kabugaw, Uba, and Magdagooc
(see Appendix 2). Jabonga vegetation is composed of wetlands, grasslands, and
secondary forest.
Dinarawan, Kabugaw, and Uba were primarily composed of secondary
forests with grassland and agricultural areas, located besides Mamanwa‘s
community, along the shore of Lake Mainit. The forest is the main source of
living for the people as it provides food, water, and income. Utilization of Kaong
[Areaga pinnata (Wurmb) Merr.], agricultural area, and the forest timber were the
observed income sources.
Magdagooc is located besides Butuan Bay. The secondary forest in the
area is dominated by Cocos nucifera L.. Coconut and fishing were the main
source of income of the people in the area.
13
23. 3.2 Sampling Method
Belt transect method and transect walk survey was utilized for this study.
All flora and grass species including the seedlings, herbs, vines, rattans, saplings
and other undergrowths of less than or equal to 3-m tall that were physically
intercepted by the transect line or those projection of foliage is intercepted by the
transect lines was identified, counted and recorded. Visual estimation of plant &
soil cover was made by ocular estimation to the nearest 1% percent. Endemic,
threatened and native species were subject for documentation during transect
walk survey. The biological method targeted the determination of the minimal
area and species area curve, density estimation, estimation of plant coverage,
and diversity measurement. A 20m transect tape was used to space successive
sampling stations. Establishment of new stations was made continuously until the
boundary of the study area are reached. Coordinates of sampling stations was
taken using the GPS receiver.
Two (2) perpendicular 1m x 1m belt transect was laid down in to each of
the transect stations established in the line intercept method. This belt transect
was described to be oriented parallel to the axis of the environmental gradient
within an area being sampled. The quadrats were placed five (5) meters apart on
both sides.
Common name, scientific name, family, and genera, abundance and direct
top coverage estimation of each species, as well as the bare ground, were
recorded.
14
24. 3.2.1 Sampling Materials
This study used a 1m X 1m transect belt made of nylon string, and 4
wooden stakes. For preservation of specimens, plastic bags and sacks, wooden
plant pressers, corrugated ventilators, blotters, newspapers, and straps were
used. A digital camera was used to photograph voucher specimens, and
sampling areas, and GPS receiver for determining coordinates of located areas
of belt transects, and track rare species of plants.
3.2.2 Species Processing and Identification
Collected samples were identified with the use of Flora of Manila, USDA
plant database, and Guide to Philippine Flora and Fauna. The identification
scheme covered at least up to the genus level. The conservation status of the
identified plants was assessed with the use of IUCN Red List for threatened
species and DAO 2007-1. Journals and publications for conservation focused in
tropical forest and vegetation in Asia and Philippines were used for further
references. Preparation of the species for herbarium purposes followed the
procedures set by Flora of Manila. Specimens for herbarium were gathered
cumulatively. Field pressing procedure was applied on the actual stations.
15
25. 3.3 Data Analysis
Ecological measurements of species composition and distribution were
evaluated by calculating the species density, frequency, dominance, and their
relative measures. Values were derived using the following formulas:
o Density = Total no. of individuals of species A / Total area sampled
o Relative Density =
o Frequency =
o Relative frequency =
o Dominance =
o Relative dominance =
o Importance Value= Relative Density + Relative Frequency + Relative
Dominance
Diversity per transect was evaluated through the use of Simpson‘s (D)
index as a measure of species richness and evenness of the community using
Microsoft QuickBASIC Application.
16
26. o Simpson‘s diversity index is calculated by this equation:
∑
D= ( )
Where: n = total no. of organisms of a particular species
N = total no. of organisms of all species
Electronic aid offered by Microsoft Excel was used for faster data
computations and analysis.
17
27. UNDERSTORY FLORA
STUDY DIVERSITY
TARGET SPECIES FOR
UNDERSTORY DIVERSITY
CONSERVATION
INDICATORS
Rare, Endemic, Endagered Grasses, Ferns, Herbs, Shrubs
Species ≤ 3 m (height)
BELT TRANSECT & AREA
METHOD QUADRAT SAMPLING
SEARCH
METRICS No. of Species Species Status
Relative Abundance,
Frequency, & Density
of Target Species
Species Diversity and
Coverage
RESULT ANALYSIS DATA ANALYSIS & CONSERVATION STATUS ASSESSMENT
Figure 2. Schematic flowchart of study, indicators, method, and metrics for assessment of the understory flora
composition, and conservation status.
18
28. 4. RESULTS AND DISCUSSION
4.1 Species Composition and Richness
Of the 406 qudrats under 11 transects in Jabonga, Agusan del Norte, two
hundred seventy-two (272) species of understory plants were collected resolved
to a total of 95 families and to two hundred ten (210) genera. On record are 9
Aroids, 1 Bromeliad, 2 Fern Allies, 12 Ferns, 19 Grasses, 42 Herbs, 2 Orchids, 4
Palms, 90 tree Saplings, 4 Sedges, 32 Shrubs, 50 Vines, 1 Weed, and 4
Zingibers. Transect 1 captured the highest number of species (83 species)
followed by Transect 9 (63 species). Transect 6 (57 species) and transect 11
captured the least number of species (43 species).
Figure 3. Total No. of Species in Understory Flora Assessment in Jabonga
90 83
80
70 63
55 55 57
60 51 52 52
49 48
50 43
40
30
20
10
0
1 2 3 4 5 6 7 8 9 10 11
TRANSECT LINE
Total no. of Species
19
29. Nephrolepsis biserrata (Sw.) Schott (Pakong Kalabaw) is the most
abundant species recording 875 individuals in 11 transects. Nephrolepsis
biserrata (Sw.) Schott are ever green perennial herb that form congested
colonies in very wet soils, along the edges of streams or marshes and are
sometimes on surfaces of lake and stagnant waters (Omojola, 1997).
Nephrolepis biserrata distribution is pantropical (Hovenkamp and Miyamoto,
2005), they are indigenous to an immense area, covering most parts of tropical
southern hemisphere and has become naturalized in almost every tropical region
of the globe. They have stems often in the form of rhizome by which they
commonly reproduce vegetatively (Robert et al, 1965). Roots are adventitious
and grow usually in clusters from the rhizome which are pteridophyte (ITIS,
2010). The leaves are commonly pinnately compound and consist of two parts:
the frond (leafy portion) and the stripe (stalk). Young developing leaves are
circinate-coiled in on themselves like a watch spring and the tip unrolls
progressively as the lower plants develop (Chee and Faiz, 1991). Nephrolepsis
biserrata have an exponential growth potential and forms dense population which
displaces native vegetation (Weber, 2003). Its fronds form a thick mat on the
ground, preventing any establishment of native plant (Weber, 2003).
Euphorbiaceae (18spp.) and Moraceae (17spp.) families had the most
number of species under 4 and 14 genera, respectively. The Moraceae (37
genera, 1100 species) is primarily a tropical to subtropical family which displays
an amazing diversity of inflorescence structures, pollination syndromes, breeding
20
30. systems, floral characters, habit, and contains several economically important
genera (Artocarpus, Brosimum, Brousonettia, Ficus, and Treculia) (Swenson et
al, 2003). Euphorbiaceae is generally distinguished by the milky sap, (When
present) unisexual (evolved) flower, ovary trilocular and superior, placentation
axile (Kothale et al, 2011).
4.2 Ecological Measurement
4.2.1 Dinarawan, San Pablo, Jabonga
4.2.1.1Transect 1
There are forty (40) quadrats positioned in Transect 1 covering a total of
five hundred eighty-six (586) individuals resolved to eighty-three (83) species.
Soleria scribiculata Nees (Arat) was the most abundant species recorded (53
individuals). Also, it is the densest species scoring 1.196 and has a relative
density of 9.39% and the most frequent species (16) with a relative frequency of
6.48%. Donax cannaeformis (G. Forst.) K. Schum (Bamban) was the most
dominant species (9.022) with a relative dominance of 11.66%.
Table 1 shows the top ten important species in the transect where Soleria
scribiculata Nees had the highest importance value of 25.554 followed by Donax
cannaeformis (G. Forst.) K. Schum and Chromoloena odorata (Hagonoy) scoring
20.397 and 14.095, respectively.
21
31. Table 1. Ecological Measurements for Transect 1 in Dinarawan, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Chromoloena odorata 8.874 2.834 2.388 14.095
Dioscorea hispida 2.048 3.644 2.949 8.641
Donax cannaeformis (G. Forst.)
3.072 5.668 11.657 20.397
K. Schum
Ficus pseudopalma Blanco 2.560 2.834 2.528 7.922
Leucosyke capitellata (Poir.)
3.242 2.834 1.404 7.481
Wedd.
Nephrolepsis biserrata (Sw.)
4.437 2.834 4.635 11.906
Schott
Saccharum spontaneum L. 7.850 2.024 1.264 11.138
Selaginella plana Hieron 3.584 4.049 4.073 11.705
Semecarpus philippinesis Engl. 1.706 2.834 3.652 8.192
Soleria scribiculata Nees 9.386 6.478 9.691 25.554
Simpson‘s Diversity Index value of 0.963 suggest that Trasect 1
understory vegetation has high diversity and there is no species that clearly
dominates area. The Species-Area Curve for Transect 1 (Figure 4) indicates that
there could be uncovered species in the area sampled. Local guides prohibited
the researcher to survey the rest of the trek in accordance to their belief that the
foregoing area is sacred.
Soleria scribiculata Nees is a sedge under Cyperaceae family, considered
to be an abundant species. The stems of Bamban (Donax) is economically
manufactured to laundry basket (FPRDI, 2012). Chromolaena odorata is
considered as one of the world‘s most invasive weeds. It produces huge
22
32. numbers of windborne seeds within 8–10 weeks after flowering (more than 80
000 seeds per plant per season). Each seed has a tuft of white hairs that allow it
to be transported by wind and water. Seeds will also attach to vehicles,
Figure 4. Transect 1 Cumulative Species-Area Curve, Dinarawan, Jabonga
90
80
70
60
Species No.
50
40
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39 41 43 45
No. of Belt Transect
machinery, clothing, footwear and animals. Most seeds germinate immediately
after rain, though some appear to remain dormant for several years (EDI, 2012).
4.2.1.2 Transect 2
There are forty (40) quadrats positioned in Transect 2 covering a total of
three hundred thirty-one (331) individuals resolved to fifty-five (55) species.
Nephrolepsis biserrata (Sw.) Schott (Pakong Kalabaw) was the most abundant
species on record (101 individuals). Also, it is the densest species scoring 2.53
and has a relative density of 30.50% and the most frequent species, appeared 27
23
33. times, with a relative frequency of 30.17%. Donax cannaeformis (G. Forst.) K.
Schum (Bamban) was the most dominant species (1.94) with a relative
dominance of 19.9%.
Table 2 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 68.02
followed by Saccharum spontaneum L. (Talahib) and Soleria scribiculata Nees
(Arat) scoring 23.46 and 15.76, respectively.
Table 2. Ecological Measurements for Transect 2 in Dinarawan, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Blumea balsamifera L. DC 1.511 2.439 4.239 8.188
Caryota mitis 2.115 3.415 3.768 9.297
Donax cannaeformis (G. Forst.) K.
Schum
2.719 4.390 5.024 12.133
Ficus pseudopalma Blanco 2.417 3.902 3.454 9.773
Ganophyllum falcatum Blume 1.813 2.927 2.512 7.094
Hypyis capitata Jacq. 6.647 4.878 4.239 15.763
Leucosyke capitellata (Poir.)
Wedd.
4.532 4.878 3.297 12.706
Nephrolepsis biserrata (Sw.)
Schott
30.514 13.171 24.333 68.017
Saccharum spontaneum L. 7.855 6.341 9.262 23.459
Soleria scribiculata Nees 6.344 7.805 4.396 18.545
Simpson‘s Diversity Index value of 0.887 suggest that Trasect 2
understory vegetation has moderate diversity and 25% of the area is nearly
dominated (24%) by Nephrolepsis biserrata (Sw.) Schott. The Cumulative
24
34. Species-Area Curve for Transect 2 (Figure 5) showed that the transect survey
covered the total species in the area sampled.
Figure 5. Transect 2 Cumulative Species-Area Curve, Dinarawan, Jabonga
60
50
40
Species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transect
Saccharum spontaneum L., an invasive Asian grass species (Graminae),
one of two wild species of sugarcane (Hammond 1999). S. spontaneum forms
dense, continuous thickets that inhibit the establishment of woody species
(Hooper et al., unpublished data) and are resistant to weed control measures due
to the species‘ deep and extensive root system. S. spontaneum resprouts
vigorously after fire (Peet, Watkinson et al. 1999; Peet, Watkinson et al. 1999).
25
35. 4.2.1.3 Transect 3
There are forty (40) quadrats positioned in Transect 2 covering a total of
three hundred thirty-one (331) individuals resolved to fifty-five (55) species.
Nephrolepsis biserrata (Sw.) Schott (Pakong Kalabaw) was the most abundant
species on record (101 individuals). Also, it is the densest species scoring 2.523
and has a relative density of 30.50% and the most frequent species, appeared 27
times, with a relative frequency of 30.17%. Donax cannaeformis (G. Forst.) K.
Schum (Bamban) was the most dominant species (1.94) with a relative
dominance of 19.9%.
Table 3. Ecological Measurements for Transect 3 in Dinarawan, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Acrostiqhum aureum L. 3.474 3.286 4.881 11.642
Cylea merrillii Diels. 2.417 5.634 2.232 10.282
Donax cannaeformis (G.
8.459 11.268 14.505 34.232
Forst.) K. Schum
Hypyis capitata Jacq. 6.042 3.286 3.208 12.536
Lygodium flexuosum (L) Sw 5.287 7.512 4.184 16.983
Nephrolepsis biserrata (Sw.)
27.341 8.451 11.158 46.950
Schott
Selaginella plana Hieron 7.553 4.225 5.579 17.357
Soleria scribiculata Nees 4.230 2.817 2.789 9.836
Thespesia populnea (L.)
2.568 4.225 3.626 10.420
Soland ex Corr.
Zoysia matrella Linn. 5.891 3.756 3.068 12.715
26
36. Table 3 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 63.56
followed by Saccharum spontaneum L. (Talahib) and Soleria scribiculata Nees
(Arat) scoring 21.77 and 17.74 respectively.
Simpson‘s Diversity Index value of 0.897 suggest that Trasect 3
understory vegetation has moderate diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 3 (Figure 6)
Figure 6. Transect 3 Cumulative Species-Area Curve, Dinarawan, Jabonga
60
50
40
Species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transect
showed that the transect survey might covered more species in the area
sampled.
4.2.1.4 Transect 4
27
37. There are forty (40) quadrats positioned in Transect 4 covering a total of
six hundred sixty (660) individuals resolved to fifty-five (55) species.
Nephrolepsis biserrata (Sw.) Schott was the most abundant species on record
(203 individuals). Also, it is the densest species scoring 5.08 and has a relative
density of 30.76% and the most frequent species, appeared 32 times, with a
relative frequency of 15.76%. It is also the most dominant species (19.87) with a
relative dominance of 22.85%.
Table 4 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 69.37
followed by Hypyis capitata Jacq. (Dilang Baka) and Donax cannaeformis (G.
Forst.) K. Schum scoring 34.30 and 18.98 respectively.
Table 4. Ecological Measurements for Transect 4 in Dinarawan, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Alpinia zerumbet (Pers.)
2.424 4.433 1.580 8.438
Burtl. & Smith
Cylea merrillii Diels. 1.818 3.448 1.437 6.703
Dinochloa luconiae (Munro)
2.727 3.941 3.161 9.829
Merr. Babuai
Donax cannaeformis (G.
7.727 4.926 6.322 18.975
Forst.) K. Schum
Hypyis capitata Jacq. 14.697 7.389 12.213 34.299
Nephrolepsis biserrata (Sw.)
30.758 15.764 22.845 69.366
Schott
Nephrolepsis hirsutula 1.818 2.463 2.586 6.867
Paspalum conjugatum Berg. 3.788 3.448 4.023 11.259
Piper aduncum 1.364 3.448 1.724 6.536
Soleria scribiculata Nees 3.939 3.941 3.736 11.616
28
38. Simpson‘s Diversity Index value of 0.871 suggest that Trasect 4
understory vegetation has moderate diversity and 25% of the area is nearly
(23%) dominated by Nephrolepsis biserrata (Sw.) Schott. The Cumulative
Species-Area Curve for Transect 4 (Figure 7) showed that the transect survey
had uncovered species in the area sampled.
Figure 7. Transect 4 Cumulative Species-Area Curve, Dinarawan, Jabonga
60
50
40
Species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transect
Hypyis capitata Jacq. is an introduced species originally from tropical
America but now pantropic, it could grow from near sea level to 750 m and is
usually found on degraded farmland and along roads and clearings in lowland
rain forest (Jacquin, 1787).
4.2.2 Kabugaw, San Pablo, Jabonga
4.2.2.1 Transect 5
29
39. There are forty (40) quadrats positioned in Transect 5 covering a total of
five hundred eighteen (518) individuals resolved to fifty-one (51) species.
Nephrolepsis biserrata (Sw.) Schott was the most abundant species on record
(61 individuals). Also, it is the densest species scoring 1.53 and has a relative
density of 11.78% and the most frequent species, appeared 22 times, with a
relative frequency of 9.74%. It is also the most dominant species (11.13) with a
relative dominance of 12.79%.
Table 5 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 34.30
followed by Hypyis capitata Jacq. and Chromoloena odorata scoring 21.46 and
19.06 respectively.
Table 5. Ecological Measurements for Transect 5 in Kabugaw, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Chromoloena odorata 8.880 4.867 5.316 19.064
Ficus pseudopalma Blanco 2.510 5.752 5.316 13.578
Hypyis capitata Jacq. 11.583 3.982 5.891 21.456
Ipomoea obscura (L.) K.G 3.282 6.195 3.448 12.925
Lygodium flexuosum (L) Sw 2.510 5.310 3.879 11.699
Nephrolepsis biserrata
11.776 9.735 12.787 34.298
(Sw.) Schott
Saccharum spontaneum L. 5.405 2.655 3.305 11.365
Selaginella plana Hieron 6.371 5.310 6.322 18.002
Soleria scribiculata Nees 7.336 4.867 4.167 16.370
Zoysia matrella Linn. 6.950 4.425 5.603 16.978
30
40. Simpson‘s Diversity Index value of 0.941 suggest that Trasect 5
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 5 (Figure 8)
showed that the transect survey covered the total species in the area sampled.
Figure 8. Transect 5 Cumulative Species-Area Curve, Kabugaw, Jabonga
60
50
40
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transect
4.2.2.2 Transect 6
There are forty-four (44) quadrats positioned in Transect 6 covering a total
of five hundred sixty-five (565) individuals resolved to fifty-seven (57) species.
Nephrolepsis biserrata (Sw.) Schott was the most abundant species on record
(99 individuals). Also, it is the densest species scoring 2.25 and has a relative
density of 17.52% and the most frequent species, appeared 26 times, with a
relative frequency of 11.00%. It is also the most dominant species (14.43) with a
relative dominance of 16.49%.
31
41. Table 6 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 45.22
followed by Hypyis capitata Jacq. and Chromoloena odorata scoring 23.26 and
25.68 respectively.
Table 6. Ecological Measurements for Transect 6 in Kabugaw, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Chromoloena odorata 3.009 3.448 2.468 8.925
Donax cannaeformis (G.
2.655 3.879 3.766 10.300
Forst.) K. Schum
Lygodium flexuosum (L)
3.717 5.172 3.117 12.006
Sw
Nephrolepsis biserrata
17.522 11.207 16.494 45.223
(Sw.) Schott
Saccharum spontaneum L. 13.097 3.017 7.143 23.257
Selaginella plana Hieron 6.195 2.586 4.156 12.937
Soleria scribiculata Nees 3.009 3.879 3.247 10.135
Spathoglottis plicata
9.558 6.897 9.221 25.675
Blurne
Thespesia populnea (L.)
2.478 4.310 2.987 9.775
Soland ex Corr.
Zoysia matrella Linn. 4.071 4.310 2.987 11.368
Simpson‘s Diversity Index value of 0.929 suggest that Trasect 6
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 6 (Figure 9)
showed that the transect survey covered the total species in the area sampled.
Figure 9. Transect 6 Cumulative Species-Area Curve, Kabugaw, Jabonga
60
50
40
Species No.
30 32
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
42. 4.2.3 Uba, San Pablo, Jabonga
4.2.3.1 Transect 7
There are forty (40) quadrats positioned in Transect 7 covering a total of
four hundred eighty-nine (489) individuals resolved to forty-eight (48) species.
Hypyis capitata Jacq. was the most abundant species on record (94 individuals).
Also, it is the densest species scoring 2.35 and has a relative density of 19.29%
and the most frequent species, appeared 17 times, with a relative frequency of
9.44%. It is also the most dominant species (9.38) with a relative dominance of
10.85%.
Table 7. Ecological Measurements for Transect 7 in Uba, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Alpinia zerumbet (Pers.)
2.258 2.222 2.894 7.374
Burtl. & Smith
Centrosema pubescens
9.647 9.444 10.999 30.090
Benth.
Chromoloena odorata 2.258 3.889 2.171 8.317
Donax cannaeformis (G.
2.668 2.778 3.618 9.064
Forst.) K. Schum
Hypyis capitata Jacq. 19.294 9.444 10.854 39.592
Ipomoea obscura (L.) K.G 1.437 3.889 2.026 7.352
Nephrolepsis biserrata (Sw.)
18.678 16.667 19.392 54.737
Schott
Paspalum conjugatum Berg. 8.621 3.889 5.933 18.443
Piper aduncum 2.258 3.333 2.460 8.051
33
43. Zoysia matrella Linn. 9.442 7.778 6.512 23.732
Table 7 shows the top ten important species in the transect where Hypyis
capitata Jacq. had the highest importance value of 39.59 followed by
Nephrolepsis biserrata (Sw.) Schott and Centrosema pubescens Benth.
(Sentrosema) scoring 54.74 and 30.09 respectively.
Simpson‘s Diversity Index value of 0.900 suggest that Trasect 7
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 7 (Figure 10)
showed that the transect survey covered the total species in the area sampled.
Figure 10. Transect 7 Cumulative Species-Area Curve, Uba, Jabonga
60
50
40
Species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39 41 43
No. of Belt Transect
Centrosema pubescens is a vigorous, trailing, twining and climbing
perennial herb with trifoliate leaves and is fairly drought tolerant (Skermann,
1988).
34
44. It is native to Central America (extending to 22° N in Mexico) and South America
(Colombia) and is introduced as forage plant near sea level to 100 m. It is widely
distributed throuout the world but it is mostly found in the New World (Ren and
Gilbert, 2010).
4.2.3.2 Transect 8
There are forty (40) quadrats positioned in Transect 8 covering a total of
five hundred fifty-nine (559) individuals resolved to fifty-two (52) species.
Nephrolepsis biserrata (Sw.) Schott was the most abundant species on record
(91 individuals). Also, it is the densest species scoring 2.28 and has a relative
density of 16.28% and the most frequent species, appeared 23 times, with a
relative frequency of 12.85%. It is also the most dominant species (14.88) with a
relative dominance of 17.07%.
Table 8. Ecological Measurements for Transect 8 in Uba, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Alpinia zerumbet (Pers.)
14.848 6.704 7.747 29.299
Burtl. & Smith
Centrosema pubescens
9.660 9.497 11.478 30.635
Benth.
Chromoloena odorata 3.220 2.793 2.296 8.309
Cyperus rotundus L. 5.188 1.117 1.435 7.740
Hypyis capitata Jacq. 5.725 2.793 4.161 12.678
Lygodium japonicum 1.431 3.352 2.152 6.935
Neotrewia cumingii
2.326 2.793 1.865 6.984
(Muell.-Arg) Pax & K.
Nephrolepsis biserrata
16.279 12.849 17.073 46.201
(Sw.) Schott
Paspalum conjugatum
2.504 2.235 3.587 8.326
Berg.
35
45. Zoysia matrella Linn. 10.197 7.263 6.169 23.629
Table 8 shows the top ten important species in the transect where
Nephrolepsis biserrata (Sw.) Schott had the highest importance value of 46.20
followed by Alpinia zerumbet (Pers.) Burtl. & Smith (Barik) and Zoysia matrella
Linn. (Barit) scoring 29.30 and 23.63 respectively.
Simpson‘s Diversity Index value of 0.921 suggest that Trasect 8
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 8 (Figure 11)
showed that the transect survey covered the total species in the area sampled.
Figure 11. Transect 8 Cumulative Species-Area Curve, Uba, Jabonga
60
50
40
Species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transect
Alpinia zerumbet (Family Zingiberaceae) is a perennial ginger growing
widely in the subtropics and tropics. It is used in folk medicine for its anti-
36
46. inflammatory, bacteriostatic, and fungistatic properties (Zoghbi, 1999). Zoysia
matrella (L.) Merr.), commonly known as Manila Grass, is one of the the most
commonly used lawn grass species and it typically grows more slowly and is less
cold-hardy, but is more tolerant to salinity and insect pests among other Zoysia
species (Patton, 2010).
4.2.3.3 Transect 9
There are forty-four (44) quadrats positioned in Transect 9 covering a total
of five hundred three (503) individuals resolved to sixty-three (63) species.
Alpinia zerumbet (Pers.) Burtl. & Smith was the most abundant species on record
(82 individuals). Also, it is the densest species scoring 2.05 and has a relative
density of 16.30% and the most frequent species, appeared 16 times, with a
relative frequency of 8.56%. It is also the most dominant species (5.13) with a
relative dominance of 6.03%.
Table 9 shows the top ten important species in the transect where Alpinia
zerumbet (Pers.) Burtl. & Smith had the highest importance value of 30.89
followed by Paspalum conjugatum Berg. (Carabao Grass) and Selaginella plana
Hieron (Kamariang Gubat) scoring 14.31 and 24.41 respectively.
Simpson‘s Diversity Index value of 0.938 suggest that Trasect 9
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 9 (Figure 12)
showed that the transect survey covered the total species in the area sampled.
37
47. Table 9. Ecological Measurements for Transect 9 in Uba, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Acrostiqhum aureum L. 3.380 4.813 4.559 12.751
Alpinia zerumbet (Pers.)
16.302 8.556 6.029 30.888
Burtl. & Smith
Arachis pentoi 4.970 1.070 2.500 8.540
Caryota cumingii Lodd. 1.789 4.278 4.412 10.479
Caryota mitis 1.789 2.674 3.971 8.434
Hypyis capitata Jacq. 7.753 4.813 5.441 18.007
Ipomoea obscura (L.) K.G 2.783 5.348 2.941 11.072
Nephrolepsis biserrata
2.783 3.209 2.500 8.492
(Sw.) Schott
Paspalum conjugatum
11.531 1.604 1.176 14.312
Berg.
Selaginella plana Hieron 7.952 7.487 8.971 24.410
Paspalum conjugatum Berg. is a species under the genus Paspalum, one
of the most complex genera containing over 400 species that are largely endemic
to the tropics and subtropics of the world (Clayton and Renvoize, 1986). In
Nigeria, P. conjugatum is one of the species which are mostly straggling plants
grown in damp open places in the genus (Lowe,1989).
Selaginella plana Hieron is a naturally spreading species of Seleinella
through human introduction (Setyawan, 2011). Aging and drought causes the
color of S. plana to become darker reddish brown than young and humid ones
(Lu and Jernstedt 1996). In Sabah, Dayaks use S. plana to treat high fever and
38
48. headache (Ahmad and Raji 1992). S. plana leaves is drunk in decoction as tonic
for treatment postpartum (Harada et al. 2002).
Figure 12. Transect 9 Cumulative Species-Area Curve, Uba, Jabonga
70
60
50
Species No.
40
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39
No. of Belt Transects
4.2.4 Magdagooc, Jabonga
4.2.4.1 Transect 10
There are forty-four (44) quadrats positioned in Transect 10 covering a
total of eight hundred forty-three (843) individuals resolved to fifty-two (52)
species. Hypyis capitata Jacq. was the most abundant species on record (135
individuals). Also, it is the densest species scoring 3.07 and has a relative
density of 16.01% and the most frequent species, appeared 28 times, with a
relative frequency of 9.89%. It is also the most dominant species (10.11) with a
relative dominance of 11.37%.
39
49. Table 10 shows the top ten important species in the transect where Hypyis
capitata Jacq. had the highest importance value of 37.28 followed by .
Nephrolepsis biserrata (Sw.) Schott and Dimeria ornithopoda Trin., Fund. Agrost.
(T Plant) scoring 33.34 and 20.08 respectively.
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Alpinia zerumbet (Pers.)
8.660 5.654 4.853 19.166
Burtl. & Smith
Chromoloena odorata 4.152 4.947 4.598 13.697
Derris elliptica Benth. 4.745 6.360 5.109 16.214
Dimeria ornithopoda Trin.,
8.778 5.300 6.003 20.081
Fund. Agrost.
Dinochloa luconiae
6.406 1.767 2.043 10.216
(Munro) Merr. Babui
Ficus pseudopalma Blanco 2.017 4.947 6.003 12.966
Hypyis capitata Jacq. 16.014 9.894 11.367 37.275
Nephrolepsis biserrata
10.676 9.894 12.771 33.342
(Sw.) Schott
Saccharum spontaneum L. 5.101 2.120 2.682 9.903
Selaginella plana Hieron 4.152 4.240 5.364 13.756
Table 10. Ecological Measurements for Transect 10 in Magdagooc, Jabonga
Simpson‘s Diversity Index value of 0.932 suggest that Trasect 10
understory vegetation has high diversity and there is no species that clearly
dominates area. The Cumulative Species-Area Curve for Transect 10 (Figure 13)
showed that the transect survey covered the total species in the area sampled.
40
50. D. ornithopoda is a widespread, polymorphic species, in which a number
of infraspecific taxa has been recognized. It is often found in streams, moist
places, and is often gregarious (Shouliang and Phillips, 2006).
Figure 13. Transect 10 Cumulative Species-Area Curve, Magdagooc, Jabonga
60
50
40
species No.
30
20
10
0
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39 41 43
No. of Belt Transects
4.2.4.2 Transect 11
There are thirty (30) quadrats positioned in Transect 11 covering a total of
three hundred fifteen (315) individuals resolved to forty-three (43) species.
Selaginella plana Hieron was the most abundant species on record (14
individuals). Also, it is the densest species scoring 2.90 and has a relative
density of 26.67% and the most frequent species, appeared 15 times, with a
41
51. relative frequency of 15.32%. It is also the most dominant species (20.52) with a
relative dominance of 22.37%.
Table 11 shows the top ten important species in the transect where
Selaginella plana Hieron had the highest importance value of 64.35 followed by
Alpinia zerumbet (Pers.) Burtl. & Smith and Begonia nigritarum Steud. scoring
25.38 and 20.11 respectively.
Table 11. Ecological Measurements for Transect 11 in Magdagooc, Jabonga
RELATIVE RELATIVE RELATIVE IMPORTANCE
SPECIES
DENSITY FREQUENCY DOMINANCE VALUE
Alpinia zerumbet (Pers.)
11.111 9.009 5.263 25.383
Burtl. & Smith
Begonia nigritarum Steud.
11.429 3.604 5.075 20.107
Spp.
Costus malorticanus 1.905 2.703 3.947 8.555
Derris elliptica Benth. 2.857 3.604 1.504 7.965
Ficus pseudopalma Blanco 1.587 4.505 2.820 8.911
Homolomena rubescens
3.175 2.703 6.767 12.644
(Roxb.) Kunth
Lygodium flexuosum (L) Sw 2.540 4.505 1.880 8.924
Nephrolepsis biserrata
5.079 5.405 5.827 16.312
(Sw.) Schott
Schimatoglottis spp. 5.397 5.405 7.707 18.509
Selaginella plana Hieron 26.667 15.315 22.368 64.350
Simpson‘s Diversity Index value of 0.893 suggest that Trasect 11
understory vegetation has moderate diversity and 25% of the area is nearly
(22%) dominated by Selaginella plana Hieron. The Cumulative Species-Area
Curve for Transect 11 (Figure 14) showed that the transect survey covered the
total species in the area sampled.
42
52. Begonia nigritarum is widely distributed in the Philippines and presents
considerable variation (Merrill, 1912). According to Hughes (2010), Begonia
nigritarum is considered doubtful, giving a total of 10 species, nine of which are
endemic in the Philippines.
Figure 14. Transect 11 Cumulative Species-Area Curve, Magdagooc, Jabonga
50
45
40
35
Species No.
30
25
20
15
10
5
0
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29
No. of Belt Transects
4.3 Diversity Index
Among the eleven (11) transect lines that were assessed, Transect 1
located at Dinarawan, Jabonga, Agusan del Norte scored the highest in
Simpson‘s Diversity Index. This value was described the understory vegetation
diversity as high. Transect 5 and 6 in Kabugaw and 7, 8, 9 10 in Uba, Jabonga
were considered also as highly diversified areas. Transect 4 followed by Transect
2, Transect 11, and Transect 3 were considered as moderately diversified.
43
53. The Simpson‘s Diversity Index ranged from 0.871 to 0.963 which indicates
that Jabonga, Agusan del Norte exhibits moderate to high diversity understory
flora composition. This also indicates that no species clearly dominates each
transect.
Figure 15. Simpson's Diversity Index of Understory Flora Vegetation in Jabonga
SIMPSON'S DIVERSITY INDEX
0.980 0.963
0.960
0.941 0.938
0.929 0.932
0.940
0.921
0.920
0.897 0.900
0.893
0.900 0.887
0.880 0.871
0.860
0.840
0.820
T1 T2 T3 T4 T5 T6 T7 T8 T9 T10 T11
4.4 Assessment of Conservation Status
IUCN ver. 2012.2 database on threatened species showed that among
the 276 species recorded, Shorea contorta (White Lawaan) is a critically
endangered species and Pterocarpus indicus Willd. Forma indicus (Smooth
Narra), Vitex parviflora Juss. (Molave), Afzelia rhomboidea (Blanco) Vid.
44
54. (Tindalo), Dillenia philippinensis Rolfe (Katmon Baging), and Alangium
longiflorum Merr. (Malatapay) are vulnerable species, while Aglaia luzoniensis
(Kuling manok) is a near threatened species.
In the list of DAO 2007-1, there is one critically endangered species,
coded as CR A1cd, in the area, the Pterocarpus indicus Willd. Forma indicus
(Smooth Narra); one endangered: and Afzelia rhomboidea (Blanco) Vidal (coded
as EN A1cd); seven are vulnerable: Vitex parviflora Juss. (Molave) (VU A1c) ,
Cynometra inaequefolia A. Gray (Dila-dila) (VU A1c) , Dillenia reifferscheidia
Naves (Katmon Kalabaw) (VU A1c), Alangium longiflorum Merr. (Malatapay) (VU
A1c), Mangifera merrillii (Pahong Liitan) (VU A1c), Shorea contorta (White
Lawaan) (VU A1cd), Securinega flexousa (Muell,-Arg.) (Anislag) (VU A1c); and
two other wildlife species: Aglaia luzoniensis (Kuling manok) and Dillenia
philippinensis Rolfe (Katmon Baging)
Pterocarpus indicus is one of the commercial tree legume species that
dominate South-East Asia and some Pacific regions (Soerianegara & Lemmens
1993). It is one of the most valuable and commonly used reforestation species in
the Philippines. It is propagated by seeds and cuttings but seedling stocks are
mainly used for reforestation and rehabilitation of denuded land areas (Rise,
1995). Pterocarpus indicus grows on a variety of soil types from fertile
agricultural soil to rocky soil, along inundated river banks, swamps and lagoons
(Allen & Allen 1981, Corner 1988). It has the status of national tree in the
Philippines and has been identified by the Forest Research Institute Malaysia
45
55. (FRIM) as one of the potential ‗millennium tree‘ species for forest plantation
establishment in Peninsular Malaysia because of its fast growth and other
desirable characteristics (Appanah & Wienland 1993, Lok 1996). The timber of P.
indicus is classified as light hardwood and is used for light to heavy construction,
joists, beams and interior finishes. The wood, which is commonly traded as
rosewood, has beautiful distinct growth rings and is ranked among the finest for
furniture making, high grade cabinet work, carvings, decorative flooring and
musical instruments (Appanah & Weinland 1993, Soerianegara & Lemmens
1993).
Pterocarpus indicus was characterized as critically endangered and coded
as CEN A1cd which indicates that the species is critically endangered as its
population is reduced in the form of an observed, estimated, inferred or
suspected reduction of at least 80% over the last 10 years or 3 generations,
whichever is the longer, based on a decline area of occupancy, extent of
occurrence and/or quality of habitat and actual or potential levels of exploitation.
According to Orwa et al (2009), Vitex parviflora Juss. occurs most
commonly in comparatively dry regions in lowland forest, often in deciduous
forest on rocky ground, on grassy slopes and on dry limestone soils, but
sometimes also in littoral rain forest or hill forest. It is usually found in regions
with distinct wet and dry seasons. The species often occur gregariously in
secondary forest and primary forest, in association with Intsia, Pahudia, Sindora,
Toona and Wrightia species. V. parviflora tolerates a wide range of soils but
46
56. occurs mostly on dry limestone soils. Vitex timber is used for high-grade
construction, interior finishing, flooring, house building, shipbuilding, railway
sleepers and carving. The wood often takes on a yellowish- green or greenish-
brown tint when boiled in water.
Vitex parviflora Juss. is coded as EN A1cd, B2bc which indicates that the
species is endangered where its population is reduced in the form of an
observerved, estimated, inferred or suspected reduction of at least 50% over the
last 10 years or 3 generations whichever is longer, based on a decline area of
occupancy, extent of occurrence and/or quality of habitat and actual or potential
levels of exploitation; and the extent of occurrence of the species is estimated to
be less than 20,000 km2 or area of occupancy is estimated to be less than 2,000
km2, and estimates indicates continuing decline, inferred, observed or projected
in area of occupancy and area, extent and/or quality of habitat (Fernando et al,
2012).
Tindalo [Afzelia rhomboidea (Blanco) Vid.] of the family Caesalpiniaceae
is an endemic tree in the country that plays an important role in ecosystem
processes such as in biochemical and hydrological cycles. It also provides
habitat for wildlife and offers protection against soil erosion (Pandey, 2002).
Tindalo is a leguminous tree species and it is considered as one of the finest
wood in the country (Florido, 2001). It belongs to the Molave type forest which is
valued for its natural beauty and durability (DENR, 2001). At present, the global
conservation status of Tindalo is endangered both on 2001 by the Genetic
47
57. Resource Conservation for Timber of the Philippines (Fernando, 2001) and in
July 2002 by the Rainforest Action Network (2002).
Afzelia rhomboidea is coded as EN A1cd, B2c which indicates that the
species is endangered where its population is reduced in the form of an
observerved, estimated, inferred or suspected reduction of at least 50% over the
last 10 years or 3 generations whichever is longer, based on a decline area of
occupancy, extent of occurrence and/or quality of habitat and actual or potential
levels of exploitation; and the extent of occurrence of the species is estimated to
be less than 20,000 km2 or area of occupancy is estimated to be less than 2,000
km2, and estimates indicates continuing decline, inferred, observed or projected
in area, extent and/or quality of habitat.
The six vulnerable species coded as VU A1c were characterized to be
plants undergone population reduction in the form of a decline in area of
occupancy, extent of occurrence and/or quality of habitat while Shorea contorta
characterized coded as VU A1cd was said to be vulnerable as it undergone
population reduction in the form of a decline in area of occupancy, extent of
occurrence and/or quality of habitat, and actual or potential levels of exploitation.
Two other wildlife species Aglaia luzoniensis and Dillenia philippinensis
Rolfe are evaluated species but does not satisfy any of the categories Critically
Endangered, Endangered, or Vulnerable but have the tendency to become
threatened due to predation and destruction of habitat. This is equivalent to the
Lower Risk, least concern category of IUCN.
48
58. Based on the conservation assessment of Guingab (1994), there are three
endemic species, and fifteen economically important species in the area (as
shown in Table 12). Endemic species is described as- the taxon is confined to a
certain geographical region or its parts thus; it is unique and found nowhere else
in the world. The Economically important species are under this criteria on the
basis of known uses, these taxon that command high economic value are prone
to extinction because they tend to be over-exploited.
Table 12. Conservation Status of Understory Flora based on (Guingab, 1994)
Scientific Name Common Name Status
Canarium asperum Benth. Pagsahingin EIS
Ficus nota (Blanco) Merr. Tibig EIS
Ficus septica Burma f. var. septica Hawili EIS
Ficus ulmifolia Lam. Isis EC/VU
Lantana camara L. Coronitas EIS
Leca guineensis G. Don Mali-Mali EIS
Leucosyke capitellata (Poir.) Wedd. Alagasi EIS
Litsea glutinosa Sablot EIS
Macaranga tanarius (Linn.) Muell.-Arg Binunga EIS
Mallotus philippinensis (Lam) Banato EIS
Melanolepis multiglandulosa (Reinw ex Blume) Alim EC/EIS
Melastoma malabathricum Linn. Malatungaw EIS
Mussaenda philippica A.Rich Kahoy Dalaga EC
Polyscias nodosa (Blume) Seem. Malapapaya EIS
Premna odorata Blanco Alagao EIS
Semecarpus philippinesis Engl. Kamiring EIS
Vitex parviflora Juss. Molave VU/EIS
The threatened species described are mainly shrubs and saplings of
trees. These species could be vulnerable to habitat fragmentation caused by
logging and kaingin, to anthropogenic pressures brought by development plans,
49
59. housing projects, encroachment of agriculture in the uplands, frequent burning,
domestic animal grazing, temperature build-up at the forest fringe, and pollution,
and to introduction of invasive alien species that dramatically alter many
ecosystems in the world.
50
60. 5. SUMMARY, CONCLUSION, AND RECOMMENDATIONS
The taxonomic understanding is critical to convene the challenges of
biodiversity conservation in the 21st century (Bhaskaran and Rajan, 2010). It is of
fundamental importance for understanding biodiversity and ecosystem
functioning, as it provides us with the data to explore and describe biodiversity
through scientific analysis. The study provides the basic information about the
understory flora species, which are currently found in Jabonga, Agusan del
Norte. Such a list could play an important role for the local and national
authorities interested in future to conserve and sustainable use the phyto-
diversity for the sustainable development of the area.
There are two hundred seventy-six (272) species of understory flora that
were recorded in Jabonga, Agusan del Norte resolved to a total of 95 families
and two hundred ten (210) genera. Of these species, thirty-three percent (33%)
were saplings, eighteen percent (18%) were vines and sixteen percent (15%)
were herbs. Euphorbiaceae (18 spp.) and Moraceae (17 spp.) family had the
most number of species that were under 4 and 14 genera, respectively. The
PAWB (1997) study recorded 219 floral species distributed in 84 genera and 78
families in the area surrounding Lake Mainit. Thus, this study extensively improve
the data recorded in the area.
Simpson‘s Diversity Index Value was calculated highest at 0.963 for
Transect 1 and lowest value of 0.871 for Transect 4 both transects are located in
51
61. Dinarawan, Jabonga. This shows that the area is moderately to highly diversified
and there is no one species that clearly dominates each transect. Such diversity
is of high priority in biodiversity conservation.
Under the National List on Threatened Philippine Plants, there is one
critically endangered species found in the area, the seedlings of Pterocarpus
indicus Willd. Forma indicus, one is endangered species, Afzelia rhomboidea
(Blanco) Vidal; seven are vulnerable: Cynometra inaequefolia A. Gray, Dillenia
reifferscheidia Naves, Alangium longiflorum Merr., Mangifera merrillii, Shorea
contorta, Securinega flexousa (Muell,-Arg.), Vitex parviflora Juss., and two are
considered as other wildlife species: Aglaia luzoniensis and Dillenia
philippinensis Rolfe. Under IUCN 2012 database Shorea contorta is a critically
endangered species and Pterocarpus indicus Willd. Forma indicus, Vitex
parviflora Juss., Afzelia rhomboidea (Blanco) Vid., Dillenia philippinensis Rolfe,
and Alangium longiflorum Merr. are vulnerable species, while Aglaia luzoniensis
is a near threatened species. These threatened species are at high risk in
possible forest exploition activities indicated by the presence of illegal logging
and kaingin. This further shows that Jabonga, Agusan del Norte deserve
consideration for urgent conservation support.
There are threatening species recorded in the area. The most abundant
species, Nephrolepsis biserrata (Sw.) Schott (Pakong Kalabaw) that dominates
73% or eight out of eleven of transects, have an exponential growth potential and
52
62. forms dense population which displaces native vegetation (Weber, 2003). Also
the presence of invasive species Chromolaena odorata (Hagonoy) and
Saccharum spontaneum L., (Talahib) with the abilities to form dense population.
Invasive species can have devastating ecological impacts and may be the
primary cause of biodiversity loss (Mack et al., 2000).
Selaganilla planna Hieron (Kamariang Gubat), a highly distributed
through human introduction, also dominates one of the transect (Transect 11).
Selaginella grow at various climatic and soil types, but generally require humidity
for better growing and need water for fertilization; its presence in an area
becomes indicator of habitat condition, including global warming and global
cooling (Setyawan, 2011).
These study compared with the dendrological assessment of the same
area of Mijares (2013), shows that there is a higher number of understorty flora
species (272) recorded than of the tree species (222). The understory flora
composition is thereby more diversed than of the tree species in the area. Thus,
the understory flora must be prioritized, in terms of biodiversity conservation,
more than the overstory flora community.
This floristic inventory is far from complete. The discovery of additional
native species is very likely and new exotic plant species could invade and
become established. It is recommended that a further exploration of the area
should be made to support preliminary results and to expand knowledge of plant
53
63. diversity and conservation. Also a continuous monitoring should be made
especially for plant species being threatened by utilization.
There is a need to increase awareness level of researchers, local
government, and communities nearby on critical flora resources and plant
diversity of the area through production and distribution of information materials,
like flyers, leaflet and the like preferably written in local dialects. Or in other
means, information dissemination regarding with the conservation and
biodiversity of the area must be done through symposiums.
Billboards to warn gatherers as a preliminary measure against illegal
cutting of plant species must be displayed around the area. A pictorial guide to
the identification of the floral species is envisioned in the near future. This should
be published to facilitate identification by students and researchers.
54
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