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Reproductive biology of Puntius denisonii, an
endemic and threatened aquarium fish of the Western Ghats and its implications
for conservation
Simmy Solomon 1, M.R. Ramprasanth 2, Fibin Baby3, Benno Pereira 4, Josin Tharian 5, Anvar Ali6 & Rajeev Raghavan 7
1,2,3,4,5,6,7 Conservation Research Group (CRG), St.
Albert’s College, Kochi, Kerala 682018, India
2 Integrated Rural Technology Center (IRTC), Mundur,
Palakkad, Kerala, India
5 Department of Zoology and Environmental Science, St.
John’s College, Anchal, Kerala 691306, India
7 Durrell Institute of Conservation and Ecology, School
of Anthropology and Conservation, University of Kent, Canterbury, Kent, CT2
7NZ, United Kingdom
Email: 1 mariyasimmy@gmail.com, 2 ramprasanthmanasam@gmail.com,3 fibinaqua@gmail.com,4 bennopereira@gmail.com,5 josinc@stjohns.ac.in,6 anvaraliif@gmail.com,7 rajeevraq@hotmail.com
(corresponding author)
Date of publication (online): 26 September 2011
Date of publication (print): 26
September 2011
ISSN 0974-7907 (online) | 0974-7893
(print)
Editor: Neelesh Dahanukar
Manuscript details:
Ms # o2608
Received 20 October 2010
Final received 13 September 2011
Finally accepted 15 September 2011
Citation: Solomon, S., M.R. Ramprasanth, F. Baby,
B. Pereira, J. Tharian, A. Ali & R. Raghavan (2011). Reproductive biology
of Puntius denisonii,
an endemic and threatened aquarium fish of the Western Ghats and its
implications for conservation. Journal
of Threatened Taxa 3(9): 2071–2077.
Copyright: © Simmy Solomon, M.R. Ramprasanth, Fibin
Baby, Benno Pereira, Josin Tharian, Anvar Ali & Rajeev Raghavan 2011.
Creative Commons Attribution 3.0 Unported License. JoTT allows unrestricted use
of this article in any medium for non-profit purposes, reproduction and
distribution by providing adequate credit to the authors and the source of
publication.
Authors: Simmy Solomon works on taxonomy and conservation of
freshwater fishes of Western Ghats. M.R.
Ramprasanth works on biology and captive breeding of indigenous
ornamental fishes of Kerala. Fibin Baby works
on taxonomy and biology of freshwater fishes of Kerala. Benno Pereira is interested in research on fish genetics and
aquaculture with an emphasis on native fishes of Kerala. Josin Tharian is interested in the
connectivity between systematic conservation planning and freshwater
biodiversity. Anvar Ali is
interested in taxonomy, systematics and biogeography of freshwater fishes of
Western Ghats. Rajeev Raghavan is
interested in research that addresses the connectivity between freshwater
biodiversity, conservation and livelihoods in Western Ghats.
Author Contributions: BP, AA and RR designed the study; SS, MRR
and FB carried out the field and laboratory work; AA, JT and RR carried out the
analysis; RR wrote the manuscript; RR was the Principal Investigator of the
projects from which the current manuscript originated.
Acknowledgements: We thank Rateesh, Naushad and Santosh for
help with the collection of samples; Shylaja Menon and Santhi P.S. (CRG, St.
Albert’s College, Kochi) for assistance in the laboratory; Ambily Nair
(University of Hasselt, Belgium) and Siby Philip (University of Porto,
Portugal) for their help during the preparation of the manuscript. Thanks are
also due to an anonymous reviewer and the subject editor for suggesting
necessary modifications that greatly improved the manuscript. Funding for this
study came from the North of England Zoological Society-Chester Zoo
Conservation Grant (UK), Critical Ecosystem Partnership Fund (CEPF)-Western
Ghats Small Grants and Columbus Zoo (Ohio- USA) Conservation Grant to the
senior author.
Abstract: This study presents
fundamental information on the reproductive biology of Puntius denisonii, an
endemic and threatened aquarium fish of the Western Ghats Hotspot. Results are based on the observations
from three river systems, Chandragiri, Valapattannam and Chaliyar. Maximum observed total length in P. denisonii was
162mm and 132mm for males and females, respectively. Males
attained sexual maturity at a lower size than females with mean size at first
maturity determined as 85.33±1.52 mm for males and 95.66±1.15 mm for females. Puntius denisoniispawned from October to March with minor differences in the peak breeding
months between the three river systems, which were studied. Sex ratio deviated significantly from 1:1 and was skewed
in favour of males. Absolute fecundity varied from 376 (fish of 102mm
total length) to 1098 (fish of 106mm total length) eggs. Currently, the closed seasons for P. denisonii have
been put in place during June, July and October based on the (mis)assumption that
the species breeds during these three months. However, the results of the present study have helped us to
understand more about the reproductive biology of the species so as to
recommend more appropriate seasonal closures. The months from October until March need to be designated as
a closed season for protecting the breeding population of P. denisonii.
Keywords:Conservation, endemic fish, Puntius
denisonii, reproduction, threatened, Western Ghats.
This article
forms part of a special series on the Western Ghats of India, disseminating the
results of work supported by the Critical Ecosystem Partnership Fund (CEPF), a
joint initiative of l’Agence Française de Développement, Conservation
International, the Global Environment Facility, the Government of Japan, the
MacArthur Foundation and the World Bank. A fundamental goal of CEPF is to
ensure civil society is engaged in biodiversity conservation. Implementation of
the CEPF investment program in the Western Ghats is led and coordinated by the
Ashoka Trust for Research in Ecology and the Environment (ATREE).
INTRODUCTION
Unsustainable
collection of endemic freshwater fish for the aquarium trade is an emerging
conservation issue in the tropics, which has resulted in the population decline
of several species such as the Asian Arowana Scleropages
formosus (Rowley et al. 2009), Silver Arowana Osteoglossum bicirrhosum (Moreau & Coomes 2006), Celestial
Pearl Danio Danio margaritatus (Roberts 2007) and Bala Shark Balantiocheilos melanopterus (Ng & Tan 1997). Nevertheless, wild caught aquarium fish
industry receives little attention from ichthyologists, local governments and
conservation organizations throughout the world, with very little research, and
no legislative controls (Moreau & Coomes 2007; Rowley et al. 2009).
The
Western Ghats (WG), an exceptional Hotspot of freshwater fish diversity and
endemism in peninsular India (Kottelat & Whitten 1996; Dahanukar et al.
2004) is an important region for aquarium fish collections (Tlusty et al.
2008). More than a hundred species
including several threatened endemics are currently collected and exported from
this region (Raghavan 2010). Similar to other parts of the world, aquarium fish collections in WG are
open access and unregulated, raising concerns about their eco-biological impact
(Raghavan 2010). Several endemic
species are known to be facing serious population decline due to indiscriminate
collections for the trade (Kurup et al. 2004; Raghavan et al. 2009).
One
such endemic species, which is currently considered to be under severe threat
from the aquarium pet trade is the Denison Barb (AKA Red Lined Torpedo Barb and
Miss Kerala), Puntius denisonii, a small- to medium- sized cyprinid having an extremely restricted distribution in the southern WG (Prasad et al. 2008). Due to its limited distributional range in the southern WG and
declining populations, P. denisonii was assigned Vulnerable
species status in the IUCN Red List (Devi & Boguskaya 2009). The recently completed IUCN Freshwater
Biodiversity Assessments in the WG has categorised this species as Endangered
(Ali et al. 2010). Nevertheless,
this species is poorly known with no information on its micro level
distribution, life history, ecology and demography (Raghavan et al. 2010). The objective of this study was to
understand the reproductive biology of P. denisonii, and discuss its implications on the conservation of wild
populations.
MATERIALS AND METHODS
Samples for the present
study were purchased from aquarium fish collectors operating in three major
rivers of the southern WG, viz., Chandragiri, Valapattannam and Chaliyar (Fig.
1) between December 2008 and November 2009. Fish were received live in packed polythene bags and
euthanized immediately by immersing in ice-slurry. Subsequently they were preserved in 4% formaldehyde and
transferred to the laboratory, where each individual was tagged, measured (Total Length TL), weighed (Total Weight TW) and sexed (by internal sexual characteristics or by examining
gonads under a dissecting microscope). Gonads were subsequently removed,
weighed (GW) and preserved in 4% formaldehyde, while matured ovaries
with visible eggs were preserved in Gilson fluid (100ml 60% alcohol, 800ml
water, 15ml 80% nitric acid, 18ml glacial acetic acid, 20g mercuric chloride)
to break down ovarian tissues.
Gonado
somatic index (GSI) was calculated as 100 XGW (TW-GW)-1 and used to delineate
the spawning season. The length at
which 50% of male and female fish were in maturing stages III and IV was taken
as the minimum length at first maturity (Bagenal 1978). Deviation from the expected 1:1 sex
ratio was analyzed using chi-square test (Corder
& Foreman 2009). Absolute
fecundity (AF) was estimated by weighing all the eggs in the ovary
and also by counting three sub samples of eggs from different parts of the
ovary. Relative fecundity (RF)
was calculated as TF/TW. Relationship of AFwith both TL and TW were determined by plotting the
points on a log-log scale as these are expected to be allometric
relationships described by a general power function y = axb, where y
is the dependent variable, x is independent variable, b is the scaling exponent
and a is the normalization constant (Kharat et al. 2008). A least square line was fitted to the
scatter of the data and the significance of the relationship was determined
from coefficient of determination (R2) and uncertainty in the
prediction of the exponent by calculating its standard error.
RESULTS
Of 1,080 fish analysed, 792
(73.33%) were mature, composed of 570 males (52.77%) and 222 females (20.55%).
Sex ratio of P. denisonii from all three rivers
deviated significantly from the expected 1:1 and was extremely skewed in favour
of males (Table 1). GSI in all three river systems peaked
during October to March with minor differences between rivers (Fig. 2). Peak maturity of P. denisonii in Chandragiri and Valapattannam rivers
were observed during December and, in the Chaliyar River during February. No temporal variation in spawning
season could be observed even though the three rivers from where the fish
samples originated were located at different latitudes (Fig. 1).
In P. denisonii, males start to mature earlier than
females (Table 1). Mean sizes at first maturity was 85.33±1.52 mm TL(male) and 95.66±1.15 mm TL (females). Absolute fecundity (AF) in P. denisonii from the Chandragiri River system varied
from 376 (102mm TL) to 1098 (106mm TL) with a mean of
762.66±264.270 eggs/fish (n=12), while relative fecundity (RF) was
between 36.11 and 94.65 with a mean of 70.44±22.79 eggs. Although we obtained several fecund
female specimens of P. denisonii from the other two rivers as well, they
were released back into the stream without sacrificing for our study. This was done taking into consideration
the threatened status of the species, and based on our assumption that the same
species may show similar range of fecundity between river systems. The
relationship of absolute fecundity with total length was best explained as logAF= 26.69 logTL – 117.3 (Fig. 3) and the relationship of absolute
fecundity with total weight was better explained as logAF= 9.55 logTW – 16.10 (Fig. 4).
DISCUSSION
Although
sex ratio of a fish may deviate from the normal 1:1 due to a number of factors (Nikolsky 1963; Alp et al. 2003) extremely
skewed ratios such as those observed in the present study are very rarely
encountered. One possible reason
for this skew in P. denisonii could be the differential habitat
occupation of the sexes. i.e., females preferring deeper waters and therefore
being less vulnerable to capture and males on the other hand living in shallow
areas from where they are easily caught. Such differential habitat occupancy by sexes has been earlier observed
in tropical fish (Macuiane et al. 2009; Lewis et al.
2005). Skewed ratios may also
occur as a result of the differences in instantaneous natural mortality between
sexes (Vincentini & Araujo 2003). However, there is no information on the demography of P. denisonii to support such an argument.
Results
obtained in this study on the spawning season are contrary to the information
in gray literature. P. denisonii was reported to spawn during June-August
with mature specimens observed from May (Radhakrishnan
& Kurup 2005). However, the
annual dynamics of GSI from three river systems of WG observed in this study
indicated that P. denisonii breeds during October to March.
As
the first step towards conservation, the State Department of Fisheries in Kerala (India) has issued an order, restricting
collection and exports of P. denisonii from the rivers of the region (Clarke et al. 2009). Several management measures including quotas, restrictions on gears,
catch size, and a seasonal closure of fishery have
been enforced (Mittal et al. 2009). Currently, the closed seasons for P. denisonii have been put in place during June, July
and October (Clarke et al. 2009) based on the
assumption that the species breeds during these three months. However, results of the present study
provide hard evidence that this seasonal closure is mistimed and has been
designed without proper understanding of the biology of this species.
Absolute
fecundity of P. denisonii is extremely low when compared to other
cyprinids such as P. sarana (Chandrasoma & de Silva 1981) and Rasbora daniconius (Nagendran et al. 1981). However, three endemic cyprinids
threatened by aquarium collections in Sri Lanka, P. nigrofasciatus, P. cumingi and P. pleurotaenia are known to have a low absolute fecundity (151–638 for 46–64 mm TL)
(de Silva & Kortmulder 1976; Chandrasoma et al. 1994) similar to P. denisonii.
As
the scale of the body increases the relationship depicting change in lengths
and weights of different body parts change as allometric relationships. As per Euclidian geometry, the lengths
of two tissues should show an exponent of one and the relationship depicting
change in length versus weight should show an exponent of 1/3 depicting
isometric relationships. Kharat et
al. (2008, p. 13) suggested that if the volume of each egg is constant, then
the fecundity should scale as unity with the ovary volume and as a result, at a
constant density, the fecundity should change as a cube of length of the fish
and as unity with weight of the fish under isometry. On the contrary, in our analysis the fecundity changed as 27thpower of length and 10th power of the weight of the fish. Our results show that the scaling
exponent of the relationship of absolute fecundity with both total length and
total weight in P. denisonii were significantly different from the
values suggested by Euclidian geometry and thus the fecundity grows
non-isometrically. As a result,
the larger fish (length and weight) have drastically more fecundity then the
slightly smaller individuals. Thus, larger specimens contribute more to reproduction in the species
and the removal of larger individuals from a population will have a drastic
impact on the demographics and subsequently on the status.
The
peculiar characters of reproduction including an extremely low absolute
fecundity and a skewed sex ratio will undoubtedly hamper natural recruitment,
influence population dynamics and lead to low population levels in P. denisonii. This cyprinid may therefore be unsuited
for large scale collections for the pet trade. The present study has also revealed that closed seasons, the
most important conservation plan for P. denisonii implemented by the local government in
Kerala is wrongly timed, and has little or no impact on the protection of wild
stocks. There is hence an urgent
need for re-designing conservation strategies for the species based on biological
information such as those generated in this study. The closed season for protecting the breeding population of P. denisonii in the rivers of northern Kerala should
be put in place from October to March.
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