Mapping of Nypa Palm Invasion of Mangrove Forest Using Low-Cost and High Resolution UAV Digital Imagery in The Niger Delta, Nigeria
Aroloye O. Numbere1*, Maitiniyazi Maimaitijiang2
1Department of Animal and Environmental
Biology, University of Port Harcourt P.M.B, Nigeria
2Department of Earth and Atmospheric Sciences, Saint Louis University, Missouri, USA
*Corresponding author: Aroloye O. Numbere, Department of Animal and Environmental Biology, University of Port Harcourt P.M.B. 5323 Choba, Nigeria. Tel: +234-8056002989; Email: aroloyen@yahoo.com
Received date: 16 March, 2019; Accepted date: 29 March, 2019; Published date: 08 April, 2019
Citation: Numbere AO, Mason
M (2019) Mapping of Nypa Palm Invasion of Mangrove Forest Using Low-Cost and
High Resolution UAV Digital Imagery in The Niger Delta, Nigeria. Curr Trends
Forest Res 6: 1031. DOI: 10.29011/2638-0013.100031
Abstract
The
encroachment of nypa palm into mangrove forest is a major cause of the
disappearance of mangrove forest in the Niger Delta. It was thus hypothesized
that the palm is an invasive species and stressor to mangrove forest and will
affect greenness and health of mangroves. The study was conducted in March,
2018 in a mixed forest (mangrove plus nypa palm) at Eagle Island. A DJI spark drone
(300 g) was flown from different geo-referenced Ground Control Points (GCP) 25 m
above the forest to record several images of tree canopies. Images from two
clear flight paths were chosen and mosaicked using software called drone deploy.
The visible atmospherically resistance index (VARI), which shows the greenness
and health of the trees were analyzed from the mosaicked images using ESRI Arc
GIS. Three Dimensional images (3D) were derived to show tree height. Result of
mangrove forest 1 indicates that significant part of the mangrove forest was
stressed because out of the VARI range of 0-1.93 (where 0=low and 1.93=high
greenness) most of the forest fell below 1.0. Similarly, result for mangrove
forest 2 show that in a range of 0-0.86 most of the forest fell below 0.5. This
indicates that the mangrove forest is stressed by the presence of the nypa
palm. However, other environmental factors such as hydrocarbon pollution may
play key role, but the result indicate that the presence of the palms increased
the stress level of the mangroves leading to decreased population. The stress
level of the mangroves can be reduced through the removal of the invasive palms
and the re-planting of mangrove propagules.
Keywords: Drone;
Invasion; Nypa palm; Unmanned Aerial vehicle; Vegetation index
Introduction
Mangroves are a biodiversity hot spot that undergo carbon sequestration
[1]. Mangrove forest is a rich source of carbon because it is a sink for carbon
dioxide. The forest purifies the environment by removing carbon dioxide, which
helps to reduce global warming effect. Carbon is found in living biomass of
tree, underground vegetation, dead mass of litter, dead wood and soil organic
matter. To control climate change different programs had been established
globally in studying the impact of climate change such as Reducing Emissions
from Deforestation and Degradation (REDD+) that adopts Measuring, Reporting and
Verification mechanisms (MRV) [2]. Tree biomass is important in monitoring
forest, and is often estimated by measuring tree height and Diameter at Breast
Height (DBH) by the use of destructive method i.e. tree cutting and weighing.
But this method is discouraged globally because it is counterproductive due to its
reduction in the number of tree stands at different geographical locations. This
is because the reduction of trees harms the environment by not reducing the
effects of atmospheric pollution, flooding and erosion. A non-destructive
method is rather preferred and known as allometric method, which involves the
use of direct measurement of the tree height and the DBH. Previous studies had
used this method to estimate Above Ground Biomass (AGB) of mangrove Rhizophoraracemosain
the Niger Delta [3]. This method employed the Model 1 (diameter-height-wood
density) mangrove biomass regression [4-6].
Remote sensing is currently being used in forestry [7,8]. It deploys
small drones or Unmanned Aerial Vehicle (UAVs), which is less expensive and
less time consuming to study different kinds of forest. Remote sensing is the
knowing, analyzing and capturing of information from a distance (RS). It is an
art used to interpret images and is a form of science, which involves the use
of mathematical models. It also involves the use of different sensor
technology. In the past low optical resolution such as MODIS and land sat [9],
and high optical resolution such as Geo eye and World view-3 had all been used
to study AGB. These methods measure horizontal, but not vertical forest
structures. However, LiDAR, an airborne sensor measures vertical structure. There
are various sensor types, the active and the passive. The active generates
their own energy and collect reflections of their own energy on earth. Examples
are RADAR (Radio Detection & Ranging) and LiDAR (Light Detection &
Ranging) whereas the passive collects and records electromagnetic energy
through optical lens. Example is digital cameras and infrared sensors that are
loaded on drones. They orbit space and collects data. Nevertheless, there are
some problems that are associated with satellite-based research such as cloud
cover which is a major problem in tropical regions such as Niger Delta where
rain falls from January to December [9]. There is also the problem of having a
suitable revisit time. For instance, Landsat revisit time is 16 days.
Similarly, satellite-based research has low resolution scenes, which mean they
get small images from space. There is also the problem of poor understory
information due to low resolution of images and high cost of scene.
The drones have therefore come to the rescue by producing high
resolution and low cost images. They are called Unmanned Aerial Vehicles (UAV).
They are light weight aircraft platform that operates from the ground. They
were originally initiated in 2006-2007 for military purpose, but are now used
for civilian purpose for resource application such as forest monitoring,
surveillance, mapping and 3D modeling amongst others. They fly manually with
the use of remote control or are preprogrammed. Drones have been used in
precision agriculture [10-12], vegetation monitoring in range land [13-15],
biodiversity monitoring [7,16], habitat monitoring[17,18], study of soil
properties[19,20], environmental monitoring [21,22], mapping and monitoring
fires [23-25], forestry [7,8], pest and disease detection [26-28] and tropical
forest conservation [29].But out of all these studies there is a limited use of
drones in the study of mangroves in the Niger Delta region, where no known
studies had been conducted.
There are three main kinds of drones according to their design and flight
mode. They include various
a.
Balloons,
blimps, kites, and paragliders.
b.
Rotary-wing
aircraft.
c.
Fixed-wing
aircraft.
The UAV has both rotary and fixed wing aircrafts. The DJI Spark Drone
used for this study is a rotary-wing aircraft. The drone has several advantages
as compared to the satellite-based system. These includes high spatial
resolution for single tree identification, high temporal resolution for time
series analysis, no problem of cloud cover effect, where it is used to generate
Digital Elevation Model (DEM), reduction of use of ground plot, operational
ease, low price for drone images, quick data acquisition, enhanced monitoring
of illegal activities such as deforestation and artisanal refining of crude oil,
access to inaccessible or remote areas, and potential environmental benefits.
Despite these advantages, there are some disadvantages of the use of drones,
these includes small payloads, low spectral resolution, poor geometric and
radiometric performance, low software automation, sensitivity to atmospheric
condition such as wind effect, short flight endurance e.g. the DJI spark drone
flies for only 16 minutes and needs the battery to be charged before reuse,
possibility of collisions since it flies at the range of ground objects,
potential problems for repairs and maintenance, need for flying licenses in
some regions, which is not a problem in the Niger Delta, safety and security
issues, potential social impacts and ethical issues.
There are different vegetation indices used to determine plant health such as Normalized Difference Vegetation Index (NDVI), Near Infra-Red (NIR) and VARI, but the significance of the NDVI is that it monitors seasonal and inter-annual changes in vegetation. For instance, lack of chlorophyll may be due to invasion pressure or pollution effect. It determines species health, climate change and pollution effect. It ranges between -1 to +1, where negative means less or no vegetation while positive means more vegetation. NDVI is equal to near infra-red minus red divided by near infrared plus red [30]. i.e.
The VARI also uses similar principle to the NDVI, they are both ratio
based index. In this study the VARI was used to determine the greenness and
health of the mangrove forest at Eagle Island. We thus hypothesized that
small drones (i.e. DJI spark drone) can be used to study the invasion of nypa
palm (Nypafruticans) in mangrove forest in the Niger Delta by checking
the greenness and health of trees.
Materials and
Methods
Description of
Study Area
The Niger Delta has a tropical monsoon climate with two seasons, dry
and wet seasons. Dry season occurs from November to January while wet season
occurs from February to October each year. But in some year’srainfall occurs
from January to December. The zone has an average annual rainfall of 1246 m. Its mangrove forest is estimated to cover an area of
5,000 to 8,500 km2[31]. Mean monthly temperature ranges between
26-30°C. The soil is swampy and grades from red to brown as a result
of iron deposition [32]. The soil compaction ranges from 0.25-0.75 tones cm-1,
while the pH ranges from 5.0-7.0. The study area is called Eagle Island in the Niger
Delta region of Nigeria (Figure1). It was an exclusive mangrove forest some 30
years ago but because of human activities invasive nypa palms had been
introduced leading to the formation of mixed forests. It is close to a river
channel that separates several small local indigenous communities. But because
of population pressure and accommodation issues in the city people had migrated
into the mangrove forest area to build and live. They cut the trees, dredged
and sand filled large portions of the forest to build houses. Because of the
intrusion of people, the mangrove forest had been converted to a mixed forest
that has a combination of palms and grass species.
Anthropogenic activities such as building, establishment of industries,
maritime transportation and trading in the locality had worsened the situation
by further opening up the forest to invasion by other alien species. The
traditional swampy mangrove soil had been converted to hard soil that is made
up of a mixture of sand and waste material. The specific area of study measures
20 m x 20 m and includes a mixture of red (Rhizophoraracemosa) and white
(Avicenniagerminans) mangroves and nypa palms (Nypafruticans).
The location is bound by river at the southern part, a tarred road separating a
boundary of an institution (Rivers State University) on the northern part, a
sand-filled area on the western part and a sewage processing company at the
eastern part.
Specification of
The DJI Spark Drone
The
DJI spark drone used for this study weighs 300 g, has a dimension of 143 x 143
x 55 mm and has a maximum speed of 31 mph. It uses a 3 D sensing system. It has
an altitude range of 0-26 ft (0-8m), an operating range of 0-96 ft (0-30m). It
has propellers and motor; and the gimbal system adjusts the camera view during
flight. The camera sensor is 12 megapixels. It takes videos and photographs. It
has a charger and flies for 16 minutes [33].
Data Acquisition
The
DJI spark drone was used for data acquisition in an area that was an exclusive
mangrove forest that was invaded by nypa palm. Some Ground Control Points (GCPs)
markers were established at the edge of the forest with boards that were painted
black and white. The different GCP were geo-referenced with Garmin GPS (USA) (Table
1). Several drone flight missions were conducted across the locations at strategic
points at the edge of the river at different time intervals from 5th
to 30thMarch, 2018. In all eight images were taken, and two clear
images were specifically chosen for data processing. These two areas are
mangrove forest sites 7 and 8 (Table 1). The aim was to derive temporal
resolutions (daily, weekly & monthly). Images were taken both automatically
and manually through the use of the remote controller. Several pictures were
taken at 25 m at the zenith with 50% overlap to enable smooth mosaicking of images.
Data Processing
The images were first mosaicked with a software called drone deploy. This
software joins each of the RGB images to make a single multiband image showing
the whole pictures of the area covered during a single flight session (Figure 2).
The mosaicked images were then used to calculate the Vegetation Atmospherically
Resistance Index (VARI), which provides information on vegetation greenness and
health status of the forest. It also provided images of the native mangrove
forest and the invasive nypa palms (Figure 2). Color patches were used to
identify the health of both species and to indicate areas with higher
chlorophyll level.
ESRI Arc GIS 9.3 [34] was used for image pre-processing to generate the
3D images from where the Above Ground Biomass (AGB), NDVI, tree height and
plant health were measured. In this study the mosaicked image was
processed with Visible Atmospherically Resistance Index (VARI). Where
VARI represents vegetation greenness and health to some extent. The
higher the value, the greener and healthier the mangrove andnypa palm trees.
Stress of invasion can reduce the greenness.
Results
The vegetation greenness/health value at mangrove forest site 7 ranges
from 0-1.93; where 0 represents low greenness and poor health while 1.93
represent highest greenness and healthy trees (Figure 3a). Similarly, at site 8
the vegetation greenness/health value ranges from 0-0.86; where 0 represents
low greenness and poor health while 1.93 represent highest greenness and
healthy trees (Figure 4a).
The mosaicked imagesare shown in Figures 3aand Figure 4awhile the processed
images using VARI is given in Figures 3b and Figure 4b. Similarly, the 3
dimensional (3D) images of tree canopy are given in Figure 5, and show the
canopy height.
Discussion
The result of this study indicates that the state of health of the
mangroves is poor because of the large presence of nypa palms. Mangroves face a
lot of environmental stressors such as pollution, invasion, salinity and
herbivory [35]. But this study used the drone image to show that areas of
mangroves invaded by the palms have less greenness due to stressors from the presence
of the palms while areas away from the palmsshow more greenness (Figure2). The
simple reason is that the palms compete with the mangroves for nutrients, and
utilize the nutrients better and faster than the mangroves due to the
configuration of their root system [36]. In figures 3a and 4aindividual
mangrove stands are surrounded by large number of nypa palm trees, thus
increasing the reduction of greenness of the mangroves, which shows high stress
level.
The mangroves and the nypa palm forest face similar environmental
stressors such as high salinity, hydrocarbon pollution, tidal surge and other
anthropogenic effects. But in addition to these problems the mangroves have the
nypa palms as one of their stressors. The study location is close to a jetty
where marine craft transports people across the sea. These sea going crafts
deposit engine oil in the sea which are carried into the mangrove forest. It is
thus inundated with human activities which contribute to the overall
degradation of the mangrove. The cutting of the trees for the purpose of fire
wood had resulted in the decimation of mangroves from this location. The drop
in the population of mangroves had further exacerbated the entry and
colonization of mangrove forest by opportunistic nypa palm [37]. The use of
drones to study invasion provides more holistic information on the health
status of the mangroves. This is better than the collection of data from the
ground alone. Therefore, as ameasure of conservation the nypa palms need to be
removed and transplanted in a different environment from the mangroves. This
will give the mangroves the breathing space to recover and grow healthier and
survive for alonger period of time. Already the mangroves are a resilient plant
that can grow in highly polluted location without dying as observed in the
Niger Delta mangroves. But their biggest challenge apart from oil and gas
exploration is invasion [37].
Conclusion
Landscape studies are better done using GIS and satellite data. But
small unmanned vehicles (drones) have proven to be very effective in retrieving
aerial images at high resolutions. In many locations around the world drones
had been deployed to study agricultural crops, tropical trees and other types
of vegetation. This is because drone images provide wider and clearer view of
tree canopies. The result of this study has shown that drones can be deployed
in studying mangrove forest, which is an improvement on the previous use of
only allometric data. Drones can also be used to study the impact of
urbanization and pollution. It can also be used to derive better carbon stock
and biodiversity data. Future study will consider the use of drones to study
canopy height and wider areas of mangroves forest to determine other stress
indices such as salinity, hydrocarbon pollution and urbanization.
Acknowledgement
We thank Mr. Chimezie Brown and Mr. Melford Agbi for assistance in sample collection.
Figure 1: Map of study area, Eagle
Island Niger Delta Nigeria.
Figure
2: Mosaicked
image of nypa palm (Nypafruticans) encroachment in a mangrove forest at
Eagle Island water front, Niger Delta, Nigeria.
Figure
3: Mangrove
forest images at site 7, showing (a) RGB imagery of mosaicked mangrove
forest; (b)Mosaicked image of mangrove forest processed with Visible
Atmospherically Resistance Index (VARI) at Eagle Island, Nigeria. Green and
yellow color indicates signs of stress whereas red color indicates healthy or
less stressed forest.
Figure
4: Mangrove
forest images at site 8 showing (a) RGB imagery of mosaicked mangrove
forest; (b) Mosaicked image of mangrove forest 8 processed with Visible
Atmospherically Resistance Index (VARI) at Eagle Island, Niger Delta Nigeria.
Green and yellow color indicates signs of stress whereas red color indicates
healthy or less stressed forest.
Figure 5: 3 D reconstruction of tree canopy of mangrove forest showing the depth and height of trees at Eagle Island, Niger Delta, Nigeria. Spatial distribution of mangrove forest due to deforestation activity.
Sites |
Class Name |
Forest type |
Coordinates of GCP |
Clarity |
Acquisition date |
1 |
Mang_UAV1 |
Mixed |
N4°47.406’; E6°58.600,
Elev. 2m |
Not clear |
5/3/2018 |
2 |
Mang_UAV2 |
Mixed |
N4°47.292’; E6°58.726;
Elev. 48m |
Not clear |
9/3/2018 |
3 |
Mang_UAV3 |
Mixed |
N4°47.230’; E6°58.558;
Elev. 15m |
Not clear |
13/3/2018 |
4 |
Mang_UAV4 |
Mixed |
N4°47.385’; E6°58.612; Elev. 12m |
Not clear |
16/3/2018 |
5 |
Mang_UAV5 |
Mixed |
N4°47.225’; E6°58.680;
Elev. 43m |
Not clear |
19/3/2018 |
6 |
Mang_UAV6 |
Mixed |
N4°47.329; E6°58.575;
Elev. 20m |
Not clear |
26/3/2018 |
7 |
Mang_UAV7 |
Mixed |
N4°47.315’; E6°58.548;
Elev. 10m |
Clear* |
30/3/2018 |
8 |
Mang_UAV8 |
Mixed |
N4°47.346’; E6°58.617;
Elev. 5m |
Clear* |
30/3/2018 |
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