Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 December 2023 | 15(12): 24437–24442
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.8242.15.12.24437-24442
#8242 | Received 29
October 2022 | Final received 07 November 2023 | Finally accepted 28 November
2023
Report of new myristica
swamp ecosystems from the Western Ghats at Pathanapuram,
Kerala, India
Niji Joseph 1, R. Sreejai 2 & M. Ajayakumar
3
1,2 DST-FIST Zoology Research Centre,
St. Stephen’s College, Pathanapuram, Pathanapuram, Kerala 689695, India.
3 Ambanar Forest Station, Pathanapuram, Kerala 689696, India.
1 nijijoseph43@gmail.com
(corresponding author), 2 sreejaiksbb@gmail.com, 3 ajayakumarmadhavan2012@gmail.com
Editor: Mandar Nilkanth Datar, MACS-Agharkar Research Institute, Pune, India. Date
of publication: 26 December 2023 (online & print)
Citation: Joseph, N., R. Sreejai & M. Ajayakumar (2023). Report of new
myristica swamp ecosystems from the Western Ghats at Pathanapuram, Kerala, India. Journal of Threatened Taxa 15(12):
24437–24442. https://doi.org/10.11609/jott.8242.15.12.24437-24442
Copyright: © Joseph et al. 2023. 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: Self-funded.
Competing interests: The authors declare no competing interests.
Author details: Niji Joseph, a PhD scholar, has a fundamental interest in benthic macroinvertebrates and forest ecosystems. Sreejai R holds the position of a professor at St. Stephen’s College, Pathanapuram, while M. Ajayakumar serves as the Deputy Forest Range Officer at Ambanar Forest Station, Pathanapuram.
Author contributions: NJ conceived the concept of the work, conducted the fieldwork, and wrote the manuscript. Revisions and editing of the work were done by SR. MA assisted in preparing the map for the article.
Acknowledgements: We would like to express our
sincere gratitude to Mr. Ajayakumar (Deputy Range
Forest Officer, Ambanar Forest Station), Vishnu V
(Reserve Forest Watcher, Punnala), Hari V Nair and Jomy Jose for their invaluable assistance during our field
visit to the site. Additionally, we extend our thanks to Mr. Biju Kumar (Deputy
Range Forest Officer, Shendurney) for generously
sharing his wealth of knowledge with us. We are also indebted to Dr. Shibu Varghese from the Department of Botany, St.
Stephen’s College, Pathanapuram, for his expertise in
identifying several plant species at the site. Furthermore, we are truly
thankful for the unwavering support and guidance provided by all the officers
from Ambanar and Punnala
forest stations. Our successful journey would not have been possible without
their assistance. I extend my heartfelt gratitude to St. Stephen’s College, Pathanapuram, for their generous provision of essential
facilities and Encouragement, pivotal to the successful completion of this
research publication.
Abstract: We present a new distributional
report of myristica swamp ecosystems in the Western
Ghats at Pathanapuram, Kerala, India based on several
distinct field surveys from April 2022 to June 2022. From Kerala, myristica swamp has previously been reported mainly from Shendurney Wildlife Sanctuary, Kulathupuzha
Reserve Forests, and adjoining regions of the Anchal
forest ranges in southern Western Ghats. The present study described and
illustrated the occurrence of myristica swamp from
the Pathanapuram forest range in Kerala for the first
time. The observed myristica swamps from the Pathanapuram forest range are seen inside the Ambanar model forest station and Punnala
forest station limits. A total of 18 myristica swamp
patches from Ambanar and seven myristica
swamps from Punnala were reported and captured. A
pilot survey from these sites suggests they are abundant with various faunal
and floral wealth. Therefore, recognition and conservation of these ecosystems
are essential and vital and suggest further surveys and conservation efforts.
Keywords: Conservation, ecological
diversity, endemic species, field survey, habitat restoration, indigenous flora
new distribution records, Pathanapuram forest range,
tropical freshwater swamps, wetland forest ecosystem.
Myristica swamps are the wetland forest ecosystems that
are inundated fully or partially for the greater part of the year. These
tropical freshwater swamps are characterized by the dominance of Myristicaceae family members like Myristica
fatua var. magnifica
(Bedd.) Sinclair and Gymnacranthera farquhariana (Wall.
ex-Hook. fil. & Thomson) Warb. (Varghese
& Menon 1999; Bhat & Kaveriappa 2009; Jose et
al. 2014a; Sujitha et al. 2019). Myristica
swamps are confined to valleys with flat bottoms and slow-moving streams in the
altitude range of 100–200 m. Myristica swamps shelter
several rare and threatened floral–faunal species (Vasudeva et al. 2001;
Ganesan 2002; Ranganathan et al. 2022). Over six decades ago, myristica swamps were initially described by Krishnamoorthy
(1960) from the Travancore region in Kerala State of southern Western Ghats.
Champion & Seth (1968) named these tropical swamps as ‘Myristica
Swamp Forest’ and categorized them under the sub group 4C. Rodgers & Panwar
(1988) emphasized the importance of conservation of the vegetation. According
to the data so far, in Kerala these swamps were mainly spanned in the valleys
of Shendurney Wildlife Sanctuary, in Kulathupuzha Reserve Forests, and adjoining regions of the Anchal forest ranges in the southern Western Ghats
(Krishnamoorthy 1960; Varghese & Kumar 1997; Varghese & Menon 1999;
Nair et al. 2007; Roby 2011; Jose et al. 2014b). In addition to Kerala, myristica swamps have also been reported from
Goa, Karnataka, and Maharashtra (Santhakumaran et al.
1995; Chandran et al. 1999; Sreedharan & Indulkar 2018). However, the once-pristine myristica swamps in the Western Ghats are presently
encountering disruption and fragmentation due to increasing growing demands for
land and water (Champion & Seth 1968; Chandran et al. 1999; Chandran &
Mesta 2001; Ranganathan et al. 2022). Increasing forest surveys in recent times
have led to the documentation of a few myristica
swamps across Western Ghats (Sreedharan & Indulkar 2018). This paper reports the identification of a
new myristica swamp ecosystems from Pathanapuram forest range in the southern part of the
Western Ghats.
We have been
sampling myristica swamp forests in southern Kerala
for a proposed study on Myristicaceae members.
On 20 April 2022, we found some canopy of Myristicaceae
members in Pathanapuram forest range (9.085340N,
76.85510E) of Punalur division in Kollam
District, Kerala, India (Figure 1). The observed Myristica
swamps from Pathanapuram Forest Range fall within Ambanar Model Forest Station and Punnala
Forest Station limits. During our first visit, we noticed the swampy habitat,
as well as the occurrence of ‘knee roots’ and ‘stilt roots’ both of which are
characteristics of myristica swamps. We have
conducted 11 field surveys during the period from April 2022–June 2022. For the
systematic study of vegetation, we chose 25 sample plots from both Ambanar and Punnala. Quadrats of
20 × 20 m were laid along the linear course of the swamps from Ambanar and Punnala respectively
for the enumeration of trees having minimum grith ≥30
cm. Girth of all trees and shrubs was calculated using a measuring tape. For
swamps smaller than 400 m2 no quadrats were placed; instead, the
species were simply listed. Both trees and underground vegetation were taken
into consideration. Two sub-quadrats of 5 × 5 m were laid for the shrub layer
within each tree quadrat (plants above one meter
height). Within each of the 5 × 5 m quadrats, two smaller quadrats of 1 × 1 m
were laid for the herb layer (plants less than one meter
height). The plant species were identified by an expert and also by comparing
pictures from published sources including the internet (Gamble & Fischer
1936; Varghese & Menon 1999; Sasidharan 2006;
Nair et al. 2007). Geographic coordinates were recorded at each sampling point
using Garmin® eTrex® 20x GPS. Image 1 shows some
individual photographs of myristica swamps from both Ambanar and Punnala Forest
Station.
The Ambanar Forest Station covers an area of 89.22587 km2.
The area of research is 0.86 ha of the total forest area. The topographic
conditions of Ambanar vary from 75–1,050 m asl. In general, red loamy soil which is rich in minerals
is found. Apart from this, alluvial soil is also found in river banks and
valleys. The degree of soil pH is 4.48–6.10. The climate of this forest area
has an air temperature of 290–310 C. Ambanar
receives annual rainfall of 2,400 mm. Humidity is highest in the months of
June, July, and August and lowest in February. The noted measures of general
relative humidity at 0830 h IST and 1730 h IST from February to March are about
52% and 98%, respectively.
The Punnala Forest Station covers an area of 49.85 km2
Compared to the surrounding level, this region has an elevation of about 10–400
m. In terms of climate, it experiences
both moderately hot as well as humid conditions. The hottest period is from
February–May and the coldest in December and January. The maximum and minimum
reported temperatures are 370C and 200C, respectively.
The area receives an average annual rainfall of 2,400 mm. The plants growing on
the hills at higher altitudes are prone to severe damage made by the dry
easterly winds. Humidity is highest in the months of June, July, and August and
lowest in February. General relative humidity at 0830 h IST and 1730 h IST
during February to March are about 52% to 98%, respectively.
All 18
patches of myristica swamps and the geographical
coordinates of the sampling points in the Ambanar
area are presented in Table 1. Geographically, all these 18 patches are located
in Manthadam region of the Ambanar.
The region Manthadam comprises a small stream that
maintains the distinctive swampy ecosystem. Olappara
and Minnaminni are the places near Manthadam in which saplings of Myristicaceae
family members are found.
In the Punnala Forest Station range, there are seven Myristica swamps present with a total area of
26.9 ha. They are Elappakkodu Bit 1, Elappakkodu Bit 2, Elappakkodu
Bit 3, Pezhummodu, Verukuzhypacha
Bit 1, Verukuzhypacha Bit 2, and Pannamood
pacha. Most of the swamps in Punnala
are inundated throughout the year due to the presence of three rivulets – Elappakkodu Thodu, Pezhumoodu Thodu, and Mukkalampadu Thodu. These three
rivulets flow into the Kallada river. Table 2 shows
the geo-coordinates of locations and the total area occupied by the myristica swamp in the Punnala
region. There were large numbers of Myristica trees
in Elappakodu swamps. Along with these seven sites,
saplings of Myristica trees grow at Choorapacha, Thulasithara, and Therdhakkara in Punnala Forest
Station. The neighbouring forest of these swamps is
semi-evergreen in nature. The Kerala Forest Development Corporation (KFDC)
Limited, Punalur Division is situated nearest to the Elappakodu swamp. Elappakodu and Pezhumood pacha are the reserved
forests in Punnala. However, some regions of Elappakodu swamp are disturbed due to locally originated
anthropogenic activities like fishing and crabbing. In Punnala
Station limits, reserve forest is much smaller and therefore more vulnerable to
local disturbances. Hence the swamps in Punnala need
special attention from a management perspective.
When
examining the vegetation listed in Table 3, Gymnacranthera
farquhariana, Myristica
fatua var. magnifica,
and Knema attenuata
(Hook.f. & Thoms.) Warb. consistently appear in both the Ambanar
and Punnala regions. These species seem to thrive in
diverse environmental conditions represented in both the areas. However, Myristica dactyloides
(Gaertn.) displays a distinct pattern, being present
in Ambanar but remarkably absent in Punnala. Our observations suggest disparities in species
distribution within Ambanar and Punnala
highlight the intricate interplay of ecological forces, suggesting a dynamic
and diverse nature shaped by a combination of microclimatic variations,
historical influences, and human activities. A comparison of the distribution
of non-Myristicaceae trees between Ambanar and Punnala shows notable
differences in species presence. Based on our preliminary findings, we recognize
the need for further investigation to better understand the disparities in
species distribution among these sites.
Myristica swamps are rich with numerous invertebrates and
vertebrates, both terrestrial and aquatic (Jose et al. 2014b;
Sinu
& Sharma 2013; Sujitha et al. 2019; Ranganathan
et al. 2022). A pilot survey from these sites suggests they are abundant with
various faunal and floral wealth. Studies documenting the biodiversity of flora
and fauna, climatic factors, hydrology, and soil, and so forth of these ranges
are not well studied and documented. For this reason, a clear picture of these
factors is not available yet. As per the pilot study, we noticed plenty of
juveniles of ecologically significant species present in these swamp forests. This
indicates that numerous species use the Myristica
swamps as breeding grounds (Abraham et al. 2018; Ranganathan et al. 2022).
Mapping and documenting the specifics of these swamp forests is both important
and potent for further research. Preventing the incursion of non-swampy plant
species into the swamp helps to maintain the swampy habitat. Raising the status
of these swamps will restrict the anthropogenic and natural disturbances. In
order to ensure a long-term monitoring, incorporating the interests of local
communities in the conservation and management activities are also desirable.
With this new reporting, the revised Indian distribution of myristica
swamps should include Ambanar and Punnala
of Pathanapuram forest range.
Table 1. List of myristica
swamps under Ambanar model forest area, Pathanapuram range.
|
|
Name of the swamp |
Geocoordinates of the swamps |
Area (Ha) |
|
|
Latitude (0N) |
Longitude (0E) |
|||
|
1 |
Manthadam Bit 1 |
90.05375 |
76.99838 |
0.8 |
|
2 |
Manthadam Bit 2 |
90.05477 |
76.99887 |
|
|
3 |
Manthadam Bit 3 |
90.05361 |
76.99866 |
|
|
4 |
Manthadam Bit 4 |
90.05344 |
76.99830 |
|
|
5 |
Manthadam Bit 5 |
90.05333 |
76.99913 |
|
|
6 |
Manthadam Bit 6 |
90.05327 |
76.99897 |
|
|
7 |
Manthadam Bit 7 |
90.05336 |
76.99883 |
|
|
8 |
Manthadam Bit 8 |
90.05322 |
76.99855 |
|
|
9 |
Manthadam Bit 9 |
90.05316 |
76.9985 |
|
|
10 |
Manthadam Bit 10 |
90.05336 |
76.99811 |
|
|
11 |
Manthadam Bit 11 |
90.05347 |
76.99772 |
|
|
12 |
Manthadam Bit 12 |
90.05344 |
76.99755 |
|
|
13 |
Manthadam Bit 13 |
90.05369 |
76.99730 |
|
|
14 |
Manthadam Bit 14 |
90.05375 |
76.99727 |
|
|
15 |
Manthadam Bit 15 |
90.05383 |
76.99736 |
|
|
16 |
Manthadam Bit 16 |
90.05383 |
76.99738 |
|
|
17 |
Manthadam Bit 17 |
90.05372 |
76.99736 |
|
|
18 |
Manthadam Bit 18 |
90.05363 |
76.99805 |
|
Table 2. List of myristica swamps under Punnala
forest area, Pathanapuram range.
|
|
Name of swamp |
Geo coordinates of the swamps |
Area (ha) |
|
|
Latitude (0N) |
Longitude (0E) |
|||
|
1 |
Elappakkodu Bit 1 |
09. 08762 |
076. 95453 |
0.87 |
|
2 |
Elappakkodu Bit 2 |
09. 08762 |
076. 95470 |
1.66 |
|
3 |
Elappakkodu Bit 3 |
09. 08922 |
076. 95295 |
0.38 |
|
4 |
Pezhumoodu |
09. 09545 |
076. 94337 |
1.99 |
|
5 |
Verukuzhypacha Bit 1 |
09. 05970 |
076. 97498 |
3.7 |
|
6 |
Verukuzhypacha Bit 2 |
09. 06812 |
076. 97509 |
5.8 |
|
7 |
Panamoodupacha |
09. 07138 |
076. 69757 |
12.5 |
Table 3. List of vegetation at Ambanar and Punnala Forest
Station.
|
Species |
Ambanar |
Punnala |
|
Myristicaceae trees |
||
|
*Gymnacranthera
farquhariana (Wall. ex-Hook. fil. &
Thomson) Warb. |
P |
P |
|
*Myristica
fatua var. magnifica (Bedd.) Sinclair |
P |
P |
|
*Knema
attenuata (Hook.f.&Thoms.) Warb |
P |
P |
|
Myristica dactyloides Gaertn |
P |
A |
|
Non Myristicaceae
trees |
||
|
*Vateria
indica L. |
P |
A |
|
Prioria pinnata (Roxb. ex-DC.) Breteler |
P |
A |
|
Neolamarckia cadamba (Roxb.) Bosser |
P |
P |
|
*Semecarpus
auriculata Bedd. |
P |
A |
|
Polyalthia fragrans (Dalzell) Hook. f. & Thomson |
P |
A |
|
Hydnocarpus pentandra (Buch -Ham.) Oken |
P |
A |
|
Homonoia riparia Lour. |
P |
A |
|
Schleichera oleosa (Lour.) Oken |
P |
P |
|
Lagerstroemia speciosa (L.) Pers. |
P |
A |
|
*Cinnamomum
malabatrum (Burm.
f.) Presl |
P |
A |
|
*Hopea
glabra Wight & Arn. |
P |
A |
|
Hopea malabarica Bedd. |
P |
A |
|
Tetrameles nudiflora R. Br. |
P |
A |
|
*Holigarna
arnottiana Hook.f. |
P |
P |
|
Diospyros buxifolia
(Blume) Hiern |
P |
A |
|
Non Myristicaceae
trees |
||
|
Syzygium gardneri Thw. |
P |
A |
|
Baccaurea courtallensis (Wight) Müll.Arg. |
P |
A |
|
Persea macrantha (Nees) Kosterm. |
A |
P |
|
*Actinodaphne
bourdillonii Gamble |
A |
P |
|
Xylia xylocarpa (Roxb.) Taub. |
A |
P |
|
*Hydnocarpus
laurifolia (Dennst.)
Sleum. |
A |
P |
|
Delonix regia (Hook.) Raf. |
A |
P |
|
Mitragyna parvifolia (Roxb.) Korth. |
A |
P |
|
Terminalia bellirica (Gaertn.) Roxb. |
A |
P |
|
Macaranga peltata (Roxb.) Müll.Arg. |
A |
P |
|
Grewia tiliaefolia Vahl |
A |
P |
|
Other vegetation |
||
|
Calamus rotang
L. |
P |
A |
|
Pandanus spp. |
P |
A |
|
Ferns |
P |
A |
|
Lagenandra ovata (L.) Thwaites |
P |
A |
|
Cheilocastus speciosus (J. Koenig) C.D. Specht |
P |
P |
|
Phrynium capitatum Willd |
A |
P |
|
Carissa carandas L. |
A |
P |
|
Colocasia esculenta (L.) Schott |
A |
P |
*Endemic
to Western Ghat
For
figure & images - - click here for full PDF
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