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Length-weight relationship and condition factor of an
endemic stone sucker, Garra
gotyla stenorhynchus(Jerdon, 1849) from two opposite flowing rivers in southern Western Ghats
Fibin
Baby 1, Josin Tharian 2, Kurian Mathew Abraham 3,
M.R. Ramprasanth 4, Anvar Ali 5 & Rajeev
Raghavan 6
1,2,4,5,6 Conservation Research Group, St. Albert’s College,
Kochi, Kerala 682018, India
2 Department of Zoology and Environmental Science, St.
John’s College, Anchal, Kerala 691306, India
3 Postgraduate and Research Department of Zoology, Mar
Thoma College, Tiruvalla, Kerala 689103, India
6 Durrell Institute of Conservation and Ecology,
University of Kent, Canterbury CT2 7NZ, United Kingdom
Email: 1 fibinaqua@gmail.com, 2 josinc@gmail.com, 3 kurianma@gmail.com, 4 ramprasanthmanasam@gmail.com, 5 anvaraliif@gmail.com, 6 rajeevraq@hotmail.com (corresponding
author)
Date of
publication (online): 26 June 2011
Date of
publication (print): 26 June 2011
ISSN
0974-7907 (online) | 0974-7893 (print)
Editor: Neelesh
Dahanukar
Manuscript details:
Ms # o2535
Received 03 August 2010
Final revised received 30 April 2011
Finally accepted 12 May 2011
Citation: Baby, F., J.
Tharian, K.M. Abraham, M.R. Ramprasanth, A. Ali & R. Raghavan (2011).
Length-weight relationship and condition factor of an endemic stone sucker, Garra
gotyla stenorhynchus (Jerdon, 1849) from two opposite flowing
rivers in southern Western Ghats . Journal of Threatened Taxa 3(6): 1851–1855.
Copyright: © Fibin
Baby, Josin Tharian, Kurian Mathew Abraham, M.R. Ramprasanth, 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.
Acknowledgements:Our study was funded by a grant from the Critical Ecosystem
Partnership Fund (CEPF) through the Western Ghats Program. We are grateful to K.K. Srivastava
(Chief Wildlife Warden, Department of Forests and Wildlife, Government of
Kerala) for permits, and to Unnikrishnan (DFO, Nilambur South); V.P. Jayprakash
(Range Officer, Karulai, Nilambur) and John Mathew (Assistant Wildlife Warden,
Silent Valley National Park) for their help with the logistics. We also thank
our colleagues at the conservation Research Group (CRG), St. Albert’s College
(Kochi), Ratheesh, Prasobh, Simmy Solomon and Shylaja Menon for their help and
assistance and to Benno Pereira for the facilities provided.
Abstract: Length
weight relationship (LWR) and condition factor were studied in Nilgiri Garra, Garra
gotyla stenorhynchus (Jerdon), from the rivers Chaliyar and
Bhavani flowing through the Western Ghats Biodiversity Hotspot. The regression equation for LWR of the
Nilgiri Garra from Chaliyar River was estimated as Log Wt = 2.920 Log L –
1.854, while those from Bhavani River as Log Wt = 2.594 Log L – 1.538. Although, the ‘b’
value observed from west flowing Chaliyar River (2.920) was higher than that
from east flowing Bhavani River (2.594), they were statistically
insignificant. Similarly, the
Condition Factor (K) was higher in Bhavani populations (2.177) compared to
Chaliyar (2.087), but were also statistically insignificant. The results indicated that populations
of G. gotyla stenorhynchus in Chaliyar
River followed an isometric like growth pattern with ‘b’ values close to cubic
law. However local populations of
the same species in Bhavani River are under stress as indicated by
comparatively lower ‘b values. This difference in ‘b’ value between the two river populations may be
due to the differences in physical habitat features of the locations from where
they were sampled, including altitude, physical habitat features, water quality
and their combined influence on the availability of food materials as well as
stock/population differences and yet to be identified stressors.
Keywords:Condition factor, Garra
gotyla stenorhynchus, length weight relationship, 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).
For figures, tables --
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The mathematical relationship between
length and weight of fishes (LWR) is a practical index suitable for
understanding their survival, growth, maturity, reproduction, and general well
being (Le Cren 1951). Information
on LWR also allows for morphological comparisons among species, or among
populations of the same species from different habitats and/or regions
(Moutopoulos & Stergiou 2002). Although estimating LWR is considered to be a regular research work of
fisheries scientists (Froese 2006), such data are currently available only for
a restricted number of species (Kulbicki et al. 2005), especially in the
Western Ghats. The same paucity of
data also applies for the information on Condition Factor (K), which compares
the well being of a fish based on the hypothesis that heavier fish of a given
length are in a better condition (Bagenal & Tesch 1978).
The Nilgiri Garra Garra gotyla stenorhynchus (Jerdon, 1849) is an
endemic stone sucker found in the streams of southern and central Western Ghats
(Dahanukar et al. 2004). G. gotyla stenorhynchus is collected and
exported to the international aquarium pet trade under the name Pincer-faced
Algae Eater (Raghavan 2010), and is also eaten by tribes and local communities
residing along the river basins where they occur (Daniels 2002). They are generally caught along with
other stream fishes, often using destructive fishing practices including
dynamiting and poisoning.
As with many endemic freshwater fish
species of the Western Ghats, there is very little information on the various
aspects of biology and population status of G. gotyla stenorhynchus in its native
range. The only previous study on
the LWR of this species (Kurup et al. 2002) is rather vague and does not
mention the sampling locations. An
attempt is therefore made to determine and compare the LWR and the condition
factor of this endemic stone sucker from two major rivers in the southern
Western Ghats.
Methods
Samples of G. gotyla stenorhynchus for the present study originated from two rivers -
Bhavani (east flowing) and Chaliyar (west flowing) (Fig. 1) of Western
Ghats. Random samples were
collected from various sites in the Bhavani drainage located in the Silent
Valley National Park, and Chaliyar drainage located in the New Amarambalam
Reserve Forest (Table 1). To avoid
sampling bias, fish were captured by the same type of gear (backpack
electro-shocker) and during the same season (between March and June 2010). Fish samples (n = 104; 60 from Bhavani
and 44 from Chaliyar) were measured for their total length (TL) and wet body
weight (WT) using digital calipers (0.01mm), and weight scale with 0.001g
accuracy at the field and released back into the stream.
The LWR was
subsequently determined using the equation W = aLb (Pauly 1984) and
logarithmically transformed into log W = log a + b log L where W is the weight
of the fish in gram and L is the total length of the fish measured in
millimeter. The parameters ‘a’ (proportionality constant) and ‘b’ (exponent) of
the LWR were estimated by least square regression (Zar 1999). The null hypothesis that b = 3 was
tested using t test as described by Zar (1999; pp.342). To test whether the power b, calculated
as a slope of the log-log plot for weight and length, was different for two
rivers, we used t test as described by Zar (1999; pp. 362). Fulton’s Condition factor (K) was
determined using the formula K = 100 W/L3 following Tesch (1971),
where W is the weight of the fish and L is the length of the fish.
The use of
electro-fishing as the sampling method meant that the total fish population of
the area could be sampled, with minimum sampling errors, and without causing
damage to the wildr stock. Size
range of specimens from Bhavani River was from 6.10mm to 18.30mm, while those
from Chaliyar River were 8.80mm to 16.47mm.
Results
The LWR of G. gotyla stenorhynchus from Chaliyar River in
the form of a regression equation was estimated as Log Wt = 2.920 Log L - 1.854
(Fig. 2), while those from Bhavani River as Log Wt = 2.594 Log L - 1.538 (Fig.
3). The ‘b’ value of Chaliyar
River (2.9203, SE = 0.1141) was not significantly different from the cubic
value as expected by isometry (t = -0.6987, df = 42, p = 0.4886). However, the ‘b’ value of Bhavani River
(2.5949, SE = 0.1063) was significantly different from the expected cubic value
(t = -3.8096, df = 58, p = 0.0003) indicating that the species does not grow
isometrically in Bhavani River. Even though the ‘b’ value of G. gotyla stenorhynchus obtained from Chaliyar
River was slightly higher than that obtained from Bhavani River (Fig. 4) the
difference was not significant (t = -1.7583, df = 100, p = 0.0818). Although the condition factor (K) (Fig.
5) of G. gotyla stenorhynchusfrom Bhavani River showed higher values (2.177) than from Chaliyar (2.087),
these were statistically insignificant (t = 0.339; p > 0.05).
Discussion
Exponent of the arithmetic form and the
slope of the regression line in the logarithmic form, ‘b’ is the most important
parameter in a LWR (Froese 2006). If ‘b = 3’, then small specimens in the samples under consideration have
the same form and condition as large specimens. If ‘b > 3’, then large
specimens have increased in height or width more than in length, either as the
result of a notable ontogenetic change in body shape with size, which is rare,
or because most large specimens in the sample were thicker than small
specimens, which is common. Conversely, if ‘b < 3’, then large specimens have changed their body
shape to become more elongated or small specimens were in better nutritional condition
at the time of sampling (Froese 2006). Differences in ‘b’ values and its variations from the ideal ‘3’ can also
arise due to variations in habitat, gonadal maturity and preservation
techniques among others (Tesch 1971; Wooton 1990). Recent evidence also indicates that LWR is also subjected to
evolutionary selection (Kharat et al. 2008). In the present study, we compared the LWR and condition
factor of G. gotyla stenorhynchusfrom two different rivers of the Western Ghats, flowing in opposite directions
- Bhavani (east flowing) and Chaliyar (west flowing).
In the present study, ‘b’ value of G. gotyla stenorhynchus from Bhavani River was
lower than (but not statistically significant) that from Chaliyar River. One of the reasons for this difference
could be the specific habitat preference of the species. G. gotyla stenorhynchus may be more suited to
the pool riffle microhabitats in lower elevation zones (90–200 m), when
compared to the rapid and cascade type of microhabitat in the higher altitudes
(500–1100 m). The energy
expenditure of the species for mobility could also be higher in the high
altitude cascade and rapid microhabitats when compared to the milder pool
riffle habitats in low elevation zones.
There are also possibilities that an
unknown stressor exists in Bhavani River as is evident from the previous
reports of skeletal deformities in freshwater fish species (Raj et al.
2004). However, we did not observe
any such morphological changes in the samples of G. gotyla stenorhynchus from this river.
It is known that the regression
coefficients for flattened fishes including those within the genus Garra are lower than the other species
(Martin-Smith 1996). This may reflect inherently higher variability in the body
shape, greater sexual dimorphism, than for heavy-bodied fishes, seasonal
changes in gonad development or some other undetermined factor (Martin-Smith
1996). A significant deviation
from the cube law and an ‘r’ value of 0.88 has been earlier reported in G. gotyla stenorhynchus (Kurup et al.
2002). However, the authors did
not provide any information on the ‘b’ value, and also as to from where the
samples were collected, thereby making it impossible to make a detailed
comparison. The same authors also
reported that G. surendranathaniihad an ‘r’ value of 0.73 and also showed deviation from the cube law (without
mentioning the ‘b’ value), and G. periyarensishad an ‘r’ value of 0.96, and that the ‘b’ value (value not mentioned) did not
significantly deviate from the ideal value of ‘3’ (Kurup et al. 2002). Both G. surendranathanii and G. periyarensis are endemic to the
Kerala region of the Western Ghats. To the best of our knowledge, there is no other study on the LWR of G. gotyla stenorhynchus. The ‘b’ values obtained in the present
study (2.92 and 2.59) are also higher than those obtained on two Southeast
Asian species of stone suckers, G. borneensis(2.45) (Martin-Smith et al 1996) and G. cambodgiensis (Mazlan et al.
2007). Although Jha et al. (2005) studied the LWR of G. gotyla gotyla from Nepal, the authors
have not provided any ‘b’ value in their results, making a comparison
difficult.
Condition factor is a useful index for the
monitoring of feeding intensity, age, and growth rates in fish (Oni et al.
1983). It is strongly influenced
by both biotic and abiotic environmental conditions and can therefore be used
as an index to assess the status of the aquatic ecosystem in which fish live
(Anene 2005). Although the
condition factor of G. gotyla stenorhynchusfrom Bhavani River was higher than from Chaliyar River (2.087), these were
statistically insignificant. The K
values of G. gotyla stenorhynchus are
however lower than those obtained for G. cambodgiensis from northern Malaysia
(Mazlan et al. 2007).
The results of the present study indicate
that populations of G. gotyla stenorhynchus in
Chaliyar River follow an isometric
like growth pattern with ‘b’ values close to cubic law and that local
populations of the same species in Bhavani River have a lower ‘b value,
deviating from the ideal ‘3’. However, there was no significant difference in
the condition factor of the species between the two rivers.
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