Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 January 2022 | 14(1): 20406–20412
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.7719.14.1.20406-20412
#7719 | Received 22
October 2021 | Finally accepted 28 December 2021
New distribution record of
globally threatened Ocean Turf Grass Halophila beccarii
Ascherson, 1871 from the North Andaman Islands
highlights the importance of seagrass exploratory surveys
Swapnali Gole
1, Prasad Gaidhani 2, Srabani Bose 3, Anant Pande
4, Jeyaraj Antony Johnson 5 & Kuppusamy
Sivakumar 6
1–6 Wildlife Institute of India, P.O.
Box 18, Chandrabani, Dehradun, Uttarakhand 248001,
India.
1 gole.swapnali@gmail.com, 2 prasadgaidhani10@gmail.com,
3 srabanibose11081995@gmail.com, 4 anant@wii.gov.in,
5 jaj@wii.gov.in, 6 ksivakumarwii@gmail.com
(corresponding author)
Editor: Anonymity
requested. Date of publication:
26 January 2022 (online & print)
Citation: Gole,
S., P. Gaidhani, S. Bose, A. Pande,
J.A. Johnson & K. Sivakumar (2022). New
distribution record of globally threatened Ocean Turf Grass Halophila beccarii Ascherson, 1871 from
the North Andaman Islands highlights the importance of seagrass exploratory
surveys. Journal of
Threatened Taxa 14(1): 20406–20412. https://doi.org/10.11609/jott.7719.14.1.20406-20412
Copyright: © Gole
et al. 2022. Creative Commons Attribution
4.0 International License. JoTT allows unrestricted use, reproduction, and distribution
of this article in any medium by providing adequate credit to the author(s) and
the source of publication.
Funding: National CAMPA Advisory
Council (NCAC), Ministry of Environment, Forest and Climate
Change, Government of India (Grant/Award Number: 13-28(01)/2015-CAMPA).
Competing interests: The authors
declare no competing interests.
Author details: Swapnali Gole is working on dugongs and
seagrasses in the Andaman Islands, as a part of the CAMPA_Dugong
Project, Wildlife Institute of India. Her doctoral research is on the ecology
of seagrass habitats and associated macro-benthic invertebrates in the Andaman
Islands. Prasad Gaidhani worked as an
intern with the Wildlife Institute of India’s CAMPA_Dugong
Project in the Andaman Islands. His primary research interests encompass
species research, community-based conservation with special emphasis on
human-wildlife conflict, across different sea/landscapes. Srabani Bose is working on seagrass and its associated microbenthic
fauna, as a part of the CAMPA Dugong Project, Wildlife Institute of India. Her
research interest in on understanding the role of benthic fauna in the critical
dugong habitat and also taxonomical study of microbenthic fauna. Anant Pande’s work is focused
on understanding drivers of population decline of marine mammal and
seabird populations, developing strategies for their conservation and
management. His work involves conducting field assessments of marine megafauna
populations to provide evidence-based inputs to policy makers. Jeyaraj Antony Johnson has been working on
taxonomy, ecology and biology of Indian fishes. His research included species
distribution patterns, community structure, spatio-temporal
changes in resource (food and space) partitioning among co-existing species,
conservation of rare and threatened species, e-flow assessment and effects of
human disturbance on aquatic resources. Currently he is coordinating the
freshwater fish monitoring project under MoEFCC’s
Long-term Ecological Observation (LTEO) programme. Sivakumar Kuppusamy
has been working on conservation and management of aquatic biodiversity
especially marine biodiversity of India as well as of Antarctica. His research
involves understanding species distribution pattern, species ecology and behavioural ecology. Currently he is coordinating the MoEFCC-CAMPA funded project on the recovery of Dugong and
its habitats in India. He has also involved in the developing a detail project
report for the Project Dolphin.
Author contributions: SG—conceptualisation
and drafting of manuscript, field work, sample collection and post processing,
data entry and analysis. PDF—field work, sample collection and post processing.
SB—laboratory work of infaunal macrobenthic
samples. AP—supervision of the field work, conceptualisation
and reviewing the manuscript. JAJ—supervision of the field work, reviewing the
manuscript. SK—study design, supervision of the field work and data analysis,
reviewing the manuscript.
Acknowledgements: This study was sponsored by
National CAMPA Advisory Council (NCAC), Ministry of Environment, Forest and
Climate Change, Government of India (Grant/Award Number: 13-28(01)/2015-CAMPA).
We acknowledge D.M. Shukla (CWLW, Department of Environment and Forests,
Andaman & Nicobar) for granting necessary work permits and assistance
provided by K.G. Rassogi, divisional forest officer (Mayabunder Wildlife Division). Our special thanks to the
frontline staff of the Mayabunder Wildlife Division; Alagar Gopi (Forest guard), Charlice
Kullu (Forest guard), Saw Tubo,
Saw Johnson, Saw Immui, Thomas, and Sumra Rao. Lastly, we thank Sohini
Dudhat (Wildlife Institute of India), Dr. Himansu Das (Environment
Agency, Abu Dhabi), Dr. Nehru Prabhakaran (Wildlife
Institute of India), and Sohom Seal (Wildlife
Institute of India) for their valuable inputs on the manuscript.
Abstract: Halophila beccarii,
listed as ‘Vulnerable’ on the IUCN Red List, aids in seagrass and mangrove
succession, acts as a substrate stabilizer and provides feeding grounds for
mega-herbivores like dugongs. This species was first recorded from the Andaman
& Nicobar Islands in 2015, and its distribution status within the
archipelago remains under-investigated. We report a new distribution record of H.
beccarii from the North Andamans and shed light
on its inter-island distribution. H. beccarii
was recorded from a mixed meadow comprising of Cymodocea
rotundata (20.5 ± 28.8%, mean seagrass
cover), Thalassia hemprichii
(16.3 ± 23.3%, mean seagrass cover), and Halodule
pinifolia (6.3 ± 12.1%, mean seagrass cover) at
Pokkadera, North and Middle Andaman district. H.
beccarii had the highest mean seagrass cover (30
± 34.7%) and shoot density (103.5 ± 68.3 shoots/ m2) among
sympatric seagrass species. We also recorded eight seagrass-associated
macrofaunal groups (gastropods, bivalves, polychaetes,
foraminiferans, nematodes, brachyurans, decapods and
asteroids) from the infaunal and epibenthic
micro-habitats within the meadow. Infaunal macrobenthos had a much higher density (73.5 ± 129.7
individuals/m2) than the epibenthic macrofauna
(0.4 ± 1.5 individuals/m2), possibly influenced by the seagrass
canopy structure and biomass. Overall, gastropods were the most dominant macrobenthic faunal group (overall mean 95.0 ± 106.1
individuals/m2). The present findings emphasize the need for more
exploratory surveys to understand H. beccarii
distribution in the Andaman & Nicobar archipelago to identify priority
conservation areas.
Keywords: Andaman & Nicobar Islands,
Dugongs, epifauna, habitat conservation, macrobenthos,
seagrass associated.
Abbreviations: ANI—Andaman & Nicobar Islands
| LIT—Line Intercept Transect.
INTRODUCTION
Seagrasses are ecosystem
engineers (Hoegh-Guldberg & Bruno 2010) that
stabilize sediments (Ondiviela et al. 2014), modify
habitats they colonize (Koch 2001) and contribute to coastal protection (Ondiviela et al. 2014). Seagrass meadows contribute to
local carbon sinks (Suchanek et al. 1985), trophic
transfer within habitats (Costanza et al. 1997), and primary production (Waycott et al. 2009), and they support a diversity of
associated invertebrate fauna (Orth et al. 1984; Lee et al. 2001; Leopardas et al. 2014; Su et al. 2020).
In India, seagrasses are
distributed along the coastlines of Gujarat, Maharashtra, Karnataka, Kerala,
Tamil Nadu, and Odisha states, and the Lakshadweep and Andaman & Nicobar
archipelagos (Thangaradjou et al. 2018). These
ecologically valuable and fragile coastal habitats are threatened in Indian
waters by high anthropogenic dependency, destructive practices like boat
anchorage, extractive fishing, and nutrient enrichment through agricultural
run-offs or domestic sewage disposal (Thangaradjou et
al. 2008; Sridhar et al. 2010; Nobi & Thangaradjou
2012). Despite being protected under the ‘Coastal Regulation Zone Act’ (Dhiman et al. 2019), seagrasses have received less
attention than other marine ecosystems (Jagtap et al.
2003).
Seagrass research in the Andaman
& Nicobar Islands (ANI) has been sporadic. Pioneering work by Jagtap (1991, 1992) and Das (1996) collectively reported
nine species. Halodule uninervis,
Thalassia hemprichii,
and Halophila ovata were the first seagrass records from ANI (Jagtap 1991), followed by new regional records of Halophila
ovalis, Cymodocea rotundata,
Enhalus acoroides, and Syringodium isoetifolium
(Jagtap 1992). Pan-Island seagrass exploratory
surveys by Das (1996) reported Cymodocea serrulata and Halodule
pinifolia, followed by a two decadal gap
in investigating species distribution status in ANI. Later, Halophila minor and
Halophila decipiens were reported from the island
waters (D’Souza et al. 2015).
The most recent addition to the
species checklist from Andaman waters is Halophila beccarii
reported from the Haddo Bay of South Andaman (Savurirajan et al. 2015). Globally, H. beccarii has a fragmented distribution range in the
Indo--Pacific region which extends from the eastern coast of Africa up to
southeastern Asia (Green & Short 2003). Although the species was first
reported from Indian waters in 1991 (Jagtap 1991),
its distribution was not known from the Andaman Islands till 2015. Furthermore,
little is known about its inter-island distribution, as records post the first
report (Savurirajan et al. 2015) are restricted to
South Andaman (Ragavan et al. 2016).
In this study, we report a new
distribution site for Halophila beccarii in
the Andaman Islands and update its current distribution status for the Andaman
group. Our study provides detailed meadow characteristics and associated
macrofaunal assemblages, and highlights the habitat importance of seagrass meadows.
STUDY AREA
The Andaman and Nicobar
archipelago is situated in the Bay of Bengal (6.750–13.683 0N and
92.2–93.95 0E) and encompasses 836 islands, islets, and rocky
outcrops with a total geographical area of 8,249 km2 (http://andaman.gov.in)
and a 1,962 km long coastline (Census Directorate 2011). The shallow waters of
the archipelago support 830 hectares of seagrass cover (Ragavan
et al. 2016).
The present study was carried out
in May 2019 as a part of a pan-island seagrass mapping survey at Pokkadera (12.9020N & 92.9100E). Pokkadera is situated on the East coast of Mayabunder (North & Middle Andaman district) in the
Andaman archipelago. It’s a large intertidal unprotected area, with a vertical
zonation expanse (distance between high to low tide when exposed) in low tide,
up to ~ 400 m. The benthic substrate profile is characterized by mixed
muddy-sandy sediment in the upper and lower intertidal zones and exposed sand
bars in the mid-intertidal area (Figure 1). Pokkadera
is an ecologically diverse site, which supports critical coastal ecosystems
like seagrass meadows, mangroves, sandy, and rocky intertidal habitats, along
with tropical littoral vegetation.
Methods
Field sampling
We carried out on-foot
exploration during low tide in the upper intertidal zone of Pokkadera.
After locating a seagrass meadow we walked the perimeter and GPS marked the
points at the edges (transition of seagrass habitat and adjacent unvegetated
sediments). Later, we plotted the
coordinates on Google Earth Pro version 7.3 to calculate the total area of the
sampled study site. We used systematic line intercept transects (LIT) to assess
seagrass meadow characteristics such as species composition, seagrass cover,
shoot density, shoot length, total biomass (above and below ground; dry
weight), and non-epiphytic algal cover (English et al. 1997). We deployed four
50 m long LITs inside the meadow, spaced apart at a distance of 150–200m. A 50
x 50 cm quadrat was placed after every 5 m interval on the LIT to record meadow
characteristics (percentage seagrass cover, species composition, non-epiphytic
algal cover). Algal shoots, independent of seagrass blades with distinct
substratum penetration, were quantified to estimate non-epiphytic algal cover
within the quadrat. We recorded seagrass-associated epibenthic macrofaunal
groups within the quadrat to estimate group densities (ind.
/m2).
We collected seagrass samples
from a 20 X 20 cm quadrat within the larger (50 x 50 cm) quadrat in each
transect (n= 3/ transect) to estimate seagrass shoot density, shoot length, and
total biomass (above and below ground; dry weight) in the laboratory. To assess
the seagrass-associated infaunal (within the
sediments) macrobenthic communities, we hand-scooped
(up to 10 cm) sediment samples in triplicates from 20 X 20 cm area, randomly
from each transect (n= 3/ transect). Seagrass and macrobenthic
sediment samples were stored in ziplock bags on the
field and transported to the laboratory for further analysis.
We also recorded environmental
parameters on the field, like pH and sea surface temperature using a hand-held
multi-parameter tester (Eutech Oaklon-
PCS Testr 35) and salinity with a handheld
refractometer (LABART).
Laboratory analysis
In the laboratory, we rinsed
seagrass samples with fresh water to remove sediment particles from the shoots
and roots. We discarded any algal shoots within the samples and thoroughly
rinsed them again. Later, we counted seagrass shoots (species-specific) present
in the samples to estimate shoot density (shoots/ m2). Further,
using a measuring scale (cm), we recorded the length of randomly picked ten
shoots to give species-specific shoot length. For Halophila beccarii, we noted additional measurements (shoot
width, n=9, and internodal length, n=6), species characteristics, and natural
history observations. Lastly, we sun-dried the seagrass samples (whole
plant, shoots, and roots) and calculated total biomass above and below ground
by dry weight (g/m2) on a micro-scale weighing balance (WENSAR
PGB-220/ 0.001 to 200 g).
Infaunal macrobenthic
analysis
We immediately preserved the macrobenthic sediments in 4% (buffered) formalin-Rose
Bengal solution and later sieved them on a 500 micron mesh to retain macrobenthic fauna (0.5mm and above; Ingole
et al. 2009). We identified the seagrass associated macrofauna
up to group level under a stereoscope (Zeiss discovery V.8) and, groups were
validated using standard identification manuals (Fauchald
1977; Keppner & Tarjan
1989; Sturm et al. 2006; Sasaki 2008). Lastly, we counted individuals of each
group to estimate their abundances.
RESULTS
We recorded four seagrass species
and eight macrobenthic groups associated with
seagrass habitats from the present study. We report a new distribution record
of globally threatened seagrass species, Halophila beccarii,
from the North Andaman region. Pokkadera seagrass
meadow spreads across ~8.2 hectares (Figure 1), comprising early-successional
species like H. beccarii, Halodule
pinifolia, and Cymodocea
rotundata; and late-successional species like Thalassia hemprichii (Vonk et al. 2015; Nowicki et al. 2017).
The mean seagrass cover in the
meadow was 18.3 ± 24.7 %, with a non-epiphytic algal cover of 18.3 ± 35 %. H.
beccarii (30 ± 34.7 %) and H. pinifolia (6.3 ± 12.1 %) contributed to the highest and
lowest seagrass cover. H. beccarii had the
highest shoot density (103.5 ± 68.3 shoots/ m2), whereas
C. rotundata added to maximum total biomass (44.0
± 56.1 g/ m--2; Table 1).
Halophila beccarii
Halophila beccarii belongs to the family Hydrocharitaceae in the order Alismatales.
The specimen recorded at the Pokkadera meadow had 4–8
lanceolate leaves with no cross venation (Image 1B & C). The mean shoot
length was 1.3 ± 0.4 cm (n= 10), mean shoot width was 1.3 ± 0.5 mm (n= 9) with
a mean internodal length of 1.7 ± 0.3 cm (n= 6). Rhizomes were smooth as
observed for the species (Image 1B).
Habitat
Halophila beccarii was distributed in the upper
intertidal zone, either as monospecific strands on sand flats or was found
associated with T. hemprichii, C. rotundata, and H. pinifolia
in a mixed species meadow (Image 1A). The species was present in intertidal
puddles or exposed on sand bars in line with previous observations (Waycott et al. 2004) and here was dominantly distributed at
the fringes of the intertidal zone, adjacent to littoral vegetation.
Associated macrobenthic
fauna
We recorded a total of eight
macrofaunal groups, both epibenthic (n= 5 groups; number of quadrats= 44) and infaunal (n= 5 groups; number of sediment samples = 12) belonging
to six phyla, associated with the seagrass beds at Pokkadera
viz; gastropods, bivalves, polychaetes, nematodes,
brachyuran, decapods, asteroids, and foraminiferans. Gastropods and bivalves were common groups
found in both the micro-habitats.
In order of abundance, gastropods
(51.4%) dominated the infaunal assemblages, followed
by bivalves (35.2%) and polychaetes (7.4%), while the
least dominant groups were nematodes (3%) and foraminifera (3%). Gastropods
were dominant in epibenthic assemblages (50%), followed by brachyurans (31.3%;
Table 2). The total mean density of epibenthic groups (0.4 ± 1.5 ind. /m2) was much lower than infaunal assemblages (73.5 ± 129.7 ind.
/m2; Table 2).
DISCUSSION
Halophila beccarii is a euryhaline species found
associated with mangrove vegetation (Jagtap 1991)
that provides numerous ecosystem services. Studies have highlighted the role of
H. beccarii meadows as sediment stabilizers,
refugia to macrobenthic and fish diversity (Mathews
et al. 2010), and pioneers for seagrass succession (Aye et al. 2014). The
species is presently listed as ‘Vulnerable’ in the IUCN Red List (Short et al.
2010) and some of the major threats are coastal infrastructure development,
marine pollution, and exploitative fishing practices, leading to modifications
of its natural habitat (Short et al. 2010).
In addition to reporting a new
distribution record, our study emphasizes the importance of mixed seagrass beds
for associated species thus, highlights the value of these coastal ecosystems.
Studies have highlighted habitat importance of H. beccarii
meadows in supporting macrobenthic diversity (Su et
al. 2020). Our findings suggest high numerical dominance of infaunal
assemblages which needs further investigation, as epifaunal and infaunal abundance in seagrass meadows is influenced by
meadow characteristics like structural complexity, canopy height, leaf
morphology, shoot density, and above and below ground biomass (Orth et al.
1984; Lee et al. 2001; Leopardas et al. 2014).
The intertidal region at Pokkadera is an unprotected area, and the seagrass habitats
are open ground for shoreline fishing activities and cattle trampling during
ebb tide, posing a threat to the existing seagrass beds, and in turn associated
fauna. Based on few anecdotal reports by local fishers, Pokkadera
is a dugong feeding habitat, which signifies the importance of the site and
adds to the necessity for habitat and species conservation.
Scientists have emphasized the
need for integrating research with policy-making to conserve H. beccarii habitats (Ramesh et al. 2018). Our work
highlights H. beccarii distribution for
prioritizing its conservation in the Andaman and Nicobar Islands, in line with
recommendations to aid ecological assessments globally (Short et al. 2010).
Lastly, we strongly recommend the need for more seagrass exploratory surveys
and long-term monitoring of critical meadows to form a robust baseline for
seagrass management in the Andaman Islands.
Table 1. Seagrass meadow
characteristics of Pokkadera seagrass meadow, Mayabunder, North and Middle Andaman district of Andaman
& Nicobar Islands.
Meadow characteristics |
Seagrass species |
|||
Halophila beccarii |
Cymodocea rotundata |
Thalassia hemprichii |
Halodule pinifolia |
|
Mean seagrass cover (%) |
30 ± 34.7 |
20.5 ± 28.8 |
16.3 ± 23.3 |
6.3 ± 12.1 |
Shoot density (shoots/ m2) |
103.5 ± 68.3 |
45.5 ± 24.4 |
40.6 ± 30 |
42.5 ± 12 |
Shoot length (cm; n= 10) |
3.2 ± 2.8 |
6.9 ± 1.7 |
5.1 ± 3.5 |
4.3 ± 1.4 |
Total Biomass (above and below;
dry weight) (g/ m2) |
1.3 ± 2.2 |
44.0 ± 56.1 |
14.1 ± 25.1 |
0.6 ± 1.8 |
Sea surface temperature- (°C)
37.3 ± 0.7 |
Salinity- (ppt) 29.0 ± 1.0 |
pH- 8.8 ± 0.1 |
(Values expressed as mean ±
standard deviation).
Table 2. Mean densities of major
seagrass-associated macrobenthic taxonomic groups
recorded at Pokkadera seagrass meadow.
Faunal groups |
Infaunal (ind. / m2) |
Epifaunal (ind.
/ m2) |
Gastropods |
188.9 ± 151.8 |
1 ± 1.7 |
Bivalves |
129.2 ± 391 |
0.1 ± 0.7 |
Polychaetes |
27.1 ± 52.2 |
not recorded |
Nematodes |
11.1 ± 26 |
not recorded |
Foraminiferans |
11.1 ± 27.4 |
not recorded |
Asteroids |
not recorded |
0.1 ± 0.7 |
Brachyurans |
not recorded |
0.6 ± 3.5 |
Decapods |
not recorded |
0.1 ± 0.7 |
For
figure & image - - click here
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