Conservation Strategies for Fish Biodiversity
Shabir Ahmad Dar, Mohd. Ashraf, Majahid khan and
A.M Najar
Ph.D scholar, Central Institute of Fisheries
Education Versova, Mumbai, India - 400061
Corresponding author: Shabir Ahmad Dar
shabirdar777@rediffmail.com
Fishes exhibit enormous diversity in size, shape,
biology and in the habitats they occupy. The great majority comprises bony
fishes, mainly teleosts. In addition, there are around 800 species of
cartilaginous and 70 of jawless fishes (lampreys and hagfishes). It is believed
that out of 4000 species of vertebrate recognised world over 22000 are fish
species; of which 8411 are fresh water while 11650 are marine. As per the report more than 24500 fin
fish species exist throughout the world. However, there is prediction of around
28500 fish species representing more half of the vertebrate diversity. They
surveys emphasised that there could well be at least 5000 species more to be
discovered.
In India 2163 species of finfish have been recorded
from upland cold (157; 7.26%), warm waters of the plain (454; 20.99%), brackish
water (182; 8.41%) and marine environment (1370; 63.3%).In terms of habitat,
fishes live in almost all conceivable aquatic habitats, ranging from Antarctic
icecap to hot springs as well as fresh to saline waters. As per the FAO, a
sustainable fisheries development envisages an eco-friendly, equitable mode of
development that can sustain livelihood over generations. An attempt has been
made to assess the current status of fish biodiversity, delineate the
threatened species of India vis-a - vis their causative factors to formulate
appropriate strategies for their conservation and rehabilitation.
Due to factors such as human modifications
to the environment, overexploitation, habitat loss, exotic species and others,
aquatic biodiversity is greatly threatened. Ecosystems and species important in
sustaining human life and the health of the environment are disappearing at an
alarming rate. In order to preserve these threatened areas and species for
future generations, immediate action in the form of aquatic biodiversity
conservation strategies are necessary. In
general, aquatic conservation strategies should support sustainable development
by protecting biological resources in ways that will preserve habitats and
ecosystems. In order for biodiversity conservation to be effective, management
measures must be broad based.
Since maintenance of fish biodiversity along with
other biotic resource has been viewed as prerequisite for the well being of
even human beings, it is essential to prevent further decline of fish resources
by devising all possible measures of conservation and rehabilitation. The
conservation policy should promote the management practices that maintain
integrity of aquatic ecosystem, prevent endangerment and enhance recovery of
the threatened species. Five principal elements or tasks in the recovery
programmes have been to be identified as
(i) Habitat management
(ii) Habitat development and maintenance
(iii)
Native fish stock
(iv)
Non native and sport
fishing
(v) Research data management and monitoring
The main goal in a conservation programme is to
conserve the genetic diversity. The fish genetic resources can be conserved by
protecting an ecosystem which is broad-based, on-specific, cost effective and
relatively simplistic in approach .It may aim in general or at specific species
like endangered or threatened ones. This can be achieved through many
mechanisms including in
situ and ex situ methods
Insitu
conservation
In situ conservation of fish as landraces and wild
relatives is useful where genetic diversity exists and where wild forms are
present. This is done through their maintenance within natural or man -made
ecosystem in which they occur. The major advantages of insitu conservation to
co-evolve with other forms, providing the breeders with a dynamic source of
resistance that is lost in ex situ conservation and (ii) natural parks and
biosphere reserves may provide less expensive protection for the wild relatives
than ex situ measures.
Ranching:
Stock enhancement through ranching is feasible only
(i) if there is incomplete colonization of available carrying capacity. The
successful induced spawning and larval rearing of endangered Tenuolosa (Hilsa) ilsha, Tor kkudree, Tor putitora, Labeo dussumieri,
Ompok pabda ,Clarias dussumieri,Ompak malabaricus, Osteobrama belangeri,
Notopterus chitala have opened up the avenues of replenishment. In the 3
important lakes, Bhimtal, Naukuchiatal and Sattal of the Kumaon Himalayas,
there are evidences of auto-stocking due to natural breeding of mahseer
fingerlings in Ladhiya and Sharda rivers by NBFGR ,Lucknow, and
National Research Centre on Cold water Fisheries (NRCCWF) Bimetal, has already
been initiated .Ranching of the pond-reared fingerlings in Pama river of Kerala
improved landings of the endangered Labeo dussumieri.
It
is felt that restocking programmes involving hatchery stocks are unlikely to
fully solve the problem since these stocks were selected for adaptation to
hatchery conditions and not to the natural environments. The hatchery stocks,
in addition, may be even inbred. Two strategies could be implemented in
restocking programmes (i) stocking spawners of domestic strain (preferably of
sex) for interbreeding with the resident population or (ii) direct stocking of
crossbred fry. However, in absence of facilities, we start with fingerlings
from the hatchery avoiding inbreeding.
Conservation aquaculture:
Through
probability of inbreeding in hatchery-bred seed normally can not be ruled out,
conservation aquaculture is gaining importance in rehabilitation programmes of
endangered / threatened fishes. It implies aquaculture in rehabilitation
programmes of endangered fish populations by increasing the effective population
size (Ne) of the threatened species .In India too, fry of the mahaseeer (
Tor putitora) have successfully been
reared from 0.20g to 105 g in about 240 days under pond environment in terrain
region of Uttaranchal State. Interestingly, sea bass (Lates calcarifer) a vulnerable species of the brackish water, has been
successfully cultured in West Bengal for about 6 months by stocking the
hatchery-produced seed.
Marine
Reserve/Protected waters:
A marine reserve is a defined space within the sea in which
fishing is banned or other restrictions are placed in an effort to protect
plants, animals, and habitats, ultimately conserving biodiversity. Marine
reserves can also be used for educational purposes, recreation, and tourism as
well as potentially increasing fisheries yields by enhancing the declining fish
populations. Marine reserves are also very similar to marine protected areas,
fishery reserves, sanctuaries, and parks.
Declaration
of certain protected areas/ biosphere reserves for in situ conservation of
resources appears to be the pragmatic approach. Reserves are a system approach
to fishery management that allows the re-establishment of age distribution and
inter and intra specific relationships like un altered community. Established
of Marine Parks is perhaps the best way for in situ conservation of marine
resources. (Established in 1980; Okha to Jodia, Gujrat coast covering 42 islands;
area 400sq. Km) (II) the Gulf of Mannar National Marine Park (III) the Wandoor
National marine park (South Andaman ; covering 10 islands ;area 282.5 sq. Km);
and Marine sanctuary -Bhitarkanika
Gahirmatha Sanctuary (Orissa) and Malvan Marine Park Sanctuary (Maharashtra).
Aquatic Diversity Management Areas (ADMAs):
The creation of ADMAs, are a systematic
management approach for watersheds, where the primary goal is to protect the
aquatic biodiversity in a given area. ADMAs range from individual species
protection acts to full-scale biodiversity oriented programs. The best way to
properly manage ADMAs is to stop or greatly reduce all human activity
contributing to habitat degradation in that area.
Bioregional Management:
Bioregional management is a total ecosystem strategy, which
regulates factors affecting aquatic biodiversity by balancing conservation,
economic, and social needs within an area. This consists of both small-scale
biosphere reserves and larger reserves. Biosphere reserves, generally small in
scale, have a strong conservation focus, and consist of one or more protected
central habitats and surrounding buffer zones. In these bio conservation units,
activities such as fishing, hunting, harvesting, and development activities are
strictly limited.
Threatened or endangered species designations:
Threatened species include organisms
likely to become endangered if not properly protected. Endangered species are
plants and animals that need protection in order to survive, as they are in
immediate danger of becoming extinct. Once species are "listed," they
become subject to national recovery programs and will be placed under
international protection. Severe monetary penalties can occur if threatened and
endangered species regulations are broken, and can even result in jail
sentences.
Local watershed groups:
Rivers
and streams, regardless of their condition, often go unprotected since they
often pass through more than one political jurisdiction, making it difficult to
enforce conservation and management of resources. However, in recent years, the
protection of lakes and small portions of watersheds organized by local
watershed groups has helped this situation. For more information on how you can
become involved in your watershed.
Freshwater Initiatives:
The Nature Conservancy has instituted a
program referred to as the Freshwater Initiative. The objective of the FWI is to
significantly increase freshwater conservation within the country, through
three strategies: watershed action, water science, and water lessons.
Specialized Programs:
Many specialized programs have been instituted
to protect biodiversity. The goal of this program is to restore the health of
riverine systems and associated species.
Research:
Various organizations and conferences that research biodiversity
and associated conservation strategies help to identify areas of future research analyze current trends in aquatic
biodiversity, even conduct specialized studies.
Increase Public Awareness:
Increasing public awareness is one of the
most important ways to conserve aquatic biodiversity. This can be accomplished
through educational programs, incentive programs, and volunteer monitoring
programs. For example, the State of Delaware has an Adopt-a-Wetland
Program designed increase public awareness as to the value and of wetlands and
the need for conservation. The EPA developed a site with links to organizations
that teach the public how to become involved in volunteer monitoring programs
at
Restoration/Mitigation Efforts:
Aquatic areas that have been damaged or
suffered habitat loss or degradation can be restored. Even species populations
that have suffered a decline can be targeted for restoration (e.g., Pacific
Northwest salmon populations). Some management practices such as the
establishment of riparian buffer zones and the restoration of natural flow
patterns and discharge regimes are being applied to riverine areas. Recently,
habitat restoration has also been performed in various areas to replace losses
from dredging projects and in many wetland habitats.
Regulatory Measures:
The
Indian Fisheries Act of 1897 (modified in 1956) is a landmark in the
conservation of fishes. Besides provision to and monitor gears, mesh size and
observance of fishing or closed seasons, the Act also prohibits the use of
explosives or poisons to indiscrimately kill fish in any water at present, the
ministry of agriculture, Government of India is modifying the Indian Fisheries
Act to incorporate all the relevant legal to conserve fish
germplasm resource. This may include wastewater
discharge regulations like NPDES or fishery conservation measures, fisheries
management councils, even fishery bans. This creation of sustainable fisheries
is largely completed through regulatory actions including the collection of the
best scientific data available.
Local community actions:
The demand for freshwater - and the threats to its health -
originate from the actions of millions of people. To solve these challenges
also requires actions of many. State and federal governments, and many local
governments and public agencies, are already at work. So, too, are numerous
citizen volunteers. Any individual can take steps to make healthy water a
welcome part of everyday life. Learn how you can make a difference.
Ex
situ conservation:
In
this measure, the threatened are conserved outside their natural habitats. The
main pillars of ex situ conservation programme are (I) live gene bank and (II)
gene bank with gamete and (III) gene bank with DNA.
Live
gene bank:
in a
live gene bank which is a genetic resource centre, the endangered species are
reared in captivity, bred therein and genetically managed avoiding inbreeding
depression, domestication and
unintended selection. The NBFGR is maintaining the wild stocks of
threatened species like Notopterus chitala,Channa marulius Tor putitora
,Labeo bata ,L dyocheilus and L. Calbasu in the Mini Germplasm Repository.Simultaneously are being made to
establish such repositories in different regions. One such has already been
established in Guwahati for in different for North-East region.
Gene
bank gamete:
In
Gamete/Embryo gene bank, adequate samples representative of the natural genetic
variation of endangered species are kept in suspended animation under extra low
temperature (-1960C) in liquid nitrogen (LN2)
availability of genetic materials of threatened categories and for intensive
breeding programmes of economically important species. Long-term
cryopreservation of milt of the endangered and economically important fishes
like Tor putitora, T.khudree,labeo
dussumieri,Labeo rohita,Catla catla cirrhinus mrigala,Cyprinus carpio
var.communis Tenualosa (Hilsa)ilisha,Horabragrus brachysoma and Oncorhynchus
mykiss has been achieved by NBFGR. Since the technique is successful only
sperm, and no method for cryopreservation of eggs/embryos has yet been
developed, it is felt that the technique is at moment only limited value in
relation to conservation of threatened species. Efforts should now be focussed
on the androgenesis through which the whole genome can be constituted from the
cryopreserved milt alone. However, the technique has enabled development of
gene bank ensuring availability of male gamete of several species all around
the year for seasonal breeders, easy transport of germplasm and genetic and
hybridization programmes.
Gene
bank with DNA:
DNA
banking which is yet to be imitated would (I)
genomic DNA (II) DNA library (genomic DNA or cDNA library (III) cloned DNA
fragments etc.
Reference
Frankham, Ballou,J.D &Briscoe,D.A (eds.).2002. A
primer of conservation genetics. Cambridge Univesity Press.Cambridge,UK.
IUCN 2009. IUCN Red List of Threatened Species.
Version 2009.).(www.iucnredlist.org).
http://www.nbfgr.res.in.
Oliney,P.J.S.,Mace,G.M &
Feistner,A.T.C.1994.Creative conservation:Interactive management of wild and
captive animals.Chapman & Hall,London.
Datta. S.N, S .K. Chakraborty. , K Venkateswaran.and
A. K. Jaiswar. 2008 .Temporal and Spatial
differences in species diversity in the intertidal region of south Mumbai.
J. Mar. Bio. Ass. India. 50(1), 29-37 pp.
Hiddink, J.G. B.R. Mackenzie, A.Rijnsdorp, N.K.Dulvy,
E.E. Nielsen, D. Bekkevold, M. Heino. P. Lorance, H. OJaveer .2008. Importance
of fish biodiversity for the management of fisheries and ecosystem. Fisheries Research, 90 (2008) 6-8.
Pielous,
E. C. 1975. Ecological diversity .Wiley Ð Interscience .New York. U.S 45 pp.
Xianshi,
J. and Qisheng, Tang. 1996. Changes in fish species diversity and dominant species
composition in the yellow sea. Fisheries Research, 26 .337-352, pp.