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<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Sustain. Food Syst.</journal-id>
<journal-title>Frontiers in Sustainable Food Systems</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Sustain. Food Syst.</abbrev-journal-title>
<issn pub-type="epub">2571-581X</issn>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fsufs.2024.1310077</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Sustainable Food Systems</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Hilsa fisheries in India: a socio-economic analysis of fishers in deltaic Ganga region of river Hooghly</article-title>
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<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Chakraborty</surname>
<given-names>Hena</given-names>
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<name>
<surname>DebRoy</surname>
<given-names>Piyashi</given-names>
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<surname>Kunui</surname>
<given-names>Arghya</given-names>
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<surname>Nandy</surname>
<given-names>Saurav Kumar</given-names>
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<surname>Jana</surname>
<given-names>Chayna</given-names>
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<name>
<surname>Sahoo</surname>
<given-names>Amiya Kumar</given-names>
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<contrib contrib-type="author" corresp="yes">
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<surname>Das</surname>
<given-names>Basanta Kumar</given-names>
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<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
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<aff><institution>ICAR - Central Inland Fisheries Research Institute</institution>, <addr-line>Kolkata, West Bengal</addr-line>, <country>India</country></aff>
<author-notes>
<fn fn-type="edited-by" id="fn0001">
<p>Edited by: Jan Van Der Ploeg, Van Hall Larenstein University of Applied Sciences, Netherlands</p>
</fn>
<fn fn-type="edited-by" id="fn0002">
<p>Reviewed by: Mohammad Jalilur Rahman, WorldFish, Bangladesh</p>
<p>Mohammad Mojibul Hoque Mozumder, University of Helsinki, Finland</p>
</fn>
<corresp id="c001">&#x002A;Correspondence: Basanta Kumar Das, <email>basantakumard@gmail.com</email></corresp>
</author-notes>
<pub-date pub-type="epub">
<day>07</day>
<month>02</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>8</volume>
<elocation-id>1310077</elocation-id>
<history>
<date date-type="received">
<day>09</day>
<month>10</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>12</day>
<month>01</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2024 Chakraborty, DebRoy, Kunui, Nandy, Jana, Sahoo and Das.</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Chakraborty, DebRoy, Kunui, Nandy, Jana, Sahoo and Das</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Hilsa (<italic>Tenualosa ilisha</italic>) is a premium table fish in the eastern and some parts of the north-eastern region of India, especially for the Bengali community, contributing uniquely to the societal and economic significance of artisanal fisheries of the country. The major distribution of the fish species in India lies in the Bhagirathi&#x2013;Hooghly component of the Ganga River system. The aim of the study was to examine if traditional Hilsa fisheries in India are sustainable as the livelihood of artisanal fishers in light of the socio-economic conditions of Hilsa fishers in West Bengal. Structured socio-economic surveys were conducted with 402 fishermen from the upper stretch of river Hooghly to its lower stretch (300&#x2009;km) in West Bengal during 2020&#x2013;2021. The average monthly income of the Hilsa fishers in the lower stretch of river Hooghly (Godakhali) (&#x20B9;25,000&#x2013;30,000/USD 301&#x2013;361) was higher than that in the upper stretch at Farakka (&#x20B9;10,000&#x2013;15,000/USD 120&#x2013;180). However, fish species other than Hilsa are generating significantly higher returns for 56% of fishers in the Hooghly district; 40% of Hilsa fishers in South 24 Parganas and Murshidabad (Farakka) districts are engaged in non-fishery activities for livelihood. There are significant differences between Hilsa fishers with other fisheries as secondary occupations and those with non-fishery activities as secondary occupations in terms of socio-economic characteristics. These imply that Hilsa fisheries are profitable as a continued traditional livelihood, but it alone is not sufficient enough to support the livelihood of the artisanal fishers. This indicates the threatened economic sustainability of the Hilsa fisheries sector at present. Considering the high market demand for Hilsa in the eastern and north-eastern regions of India and the market complexities, more significant investments need to be channeled into the Hilsa fisheries of the northern Bay of Bengal region. Such investments encompass a wholesome approach, including more governmental initiatives for conservation and management.</p>
</abstract>
<kwd-group>
<kwd>socio-economics</kwd>
<kwd>Hilsa</kwd>
<kwd>fishermen</kwd>
<kwd>Hooghly</kwd>
<kwd>livelihood</kwd>
</kwd-group>
<counts>
<fig-count count="3"/>
<table-count count="5"/>
<equation-count count="0"/>
<ref-count count="47"/>
<page-count count="10"/>
<word-count count="8032"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Land, Livelihoods and Food Security</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="sec1">
<label>1</label>
<title>Introduction</title>
<p>Hilsa (<italic>Tenualosa ilisha</italic>), also known as Hilsa shad (family Clupeidae), is a premium table fish of India (<xref ref-type="bibr" rid="ref18">Dutta et al., 2021</xref>). It contributes to the cultural, societal, and economic significance of West Bengal in the eastern region of India and Assam and Tripura in the north-eastern region (<xref ref-type="bibr" rid="ref21">Hossain et al., 2020</xref>). Salt-fermented Hilsa, locally known as <italic>lonailish,</italic> is a relished delicacy in the north-eastern region (<xref ref-type="bibr" rid="ref29">Majumdar et al., 2016</xref>). Hilsa is a rich source of omega-3 PUFAs, EPA, DHA, and high-quality proteins (<xref ref-type="bibr" rid="ref37">Sahoo et al., 2018</xref>). Apart from India, Hilsa is biologically, nutritionally, economically, socially, and culturally significant in Bangladesh, Myanmar, and the Persian Gulf (<xref ref-type="bibr" rid="ref34">Rahman et al., 2020</xref>; <xref ref-type="bibr" rid="ref2">Ahmed et al., 2021</xref>). Hilsa is found in rivers, estuaries, and coastal waters. The deltaic habitats of river Ganga spanning the northern Bay of Bengal is a rich source of Hilsa fishery, the life cycle of Hilsa being partially marine (<xref ref-type="bibr" rid="ref27">Lauria et al., 2018</xref>) and anadromous in nature. In fact, the highest catch of Hilsa in India comes from the deltaic Ganga region in the coastal Bay of Bengal (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). The primary distribution of this fish species in India lies in the Bhagirathi&#x2013;Hooghly component of the Ganga River system (<xref ref-type="bibr" rid="ref5">Bhaumik, 2017</xref>; <xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>).</p>
<p>Hilsa fisheries provide a high social impact in the Ganga&#x2013;Brahmaputra&#x2013;Meghna basin of the northern part of the Bay of Bengal because of its high abundance, where 250 million people, directly and indirectly, depend on this species. In Bangladesh, the non-consumptive value of Hilsa has been reported to range from USD 167.5 million to USD 355.7 million <italic>per annum</italic>, where poor people place the highest value on Hilsa fishery restoration (<xref ref-type="bibr" rid="ref31">Mohammed et al., 2016</xref>). It is the source of livelihood for 0.46 million fishers of West Bengal in India. The consumption of Hilsa is culturally significant for the Bengali community in weddings, festivities, and religious ceremonies. There are also indigenous knowledge bases related to Hilsa that if the winds blow from the east, Hilsa will be available in large quantities (<xref ref-type="bibr" rid="ref39">Sharma et al., 2019</xref>).</p>
<p>The major producers of Hilsa in the world are Bangladesh (76%), Myanmar (15%), and India (4%), contributing 95% of the global Hilsa catches (<xref ref-type="bibr" rid="ref21">Hossain et al., 2020</xref>). The remaining 5% is shared by Iraq, Iran, Kuwait, Thailand, Myanmar, and Pakistan. If the recently available data for capturing fisheries from FAO in 2021 are taken into account, it is further estimated that the share of Bangladesh to global Hilsa production has increased to 97.01% and that of India has shrunk to 2.41% (<xref ref-type="bibr" rid="ref19">FAO, 2023</xref>). The global average production of Hilsa was about 5.83 lakh tonnes in 2021, with Bangladesh having the highest production of 5.65 lakh tonnes (<xref ref-type="bibr" rid="ref19">FAO, 2023</xref>). The annual production of Hilsa in India in 2021 was 0.14 lakh tonnes (<xref ref-type="bibr" rid="ref19">FAO, 2023</xref>; <xref rid="SM1" ref-type="supplementary-material">Supplementary material</xref>). It was estimated that Hilsa contributes 14% to the fish catch of river Hooghly and 23% to that of the Narmada estuarine system (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). The northern Bay of Bengal and its associated river systems contribute to 90% of Hilsa catch in the country (<xref ref-type="bibr" rid="ref14">CMFRI, 2016</xref>). Hilsa accounts for 12.5% of the fish catch (<xref ref-type="bibr" rid="ref20">Hossain et al., 2019</xref>) in West Bengal in India. A significant chunk of the Hilsa population is also found along the Narmada and Tapti estuaries. Hilsa was also reported as available in Mahanadi estuary (<xref ref-type="bibr" rid="ref24">Jhingran and Natarajan, 1969</xref>; <xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>), river Brahmaputra (<xref ref-type="bibr" rid="ref44">Vass and Moza, 2011</xref>; <xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>; <xref ref-type="bibr" rid="ref47">Yadav et al., 2022a</xref>,<xref ref-type="bibr" rid="ref46">b</xref>), river Narmada (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>; <xref ref-type="bibr" rid="ref4">Bhakta et al., 2018</xref>), river Tapti (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>), Vallabh Sagar (Ukai) reservoir (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>), river Godavari (<xref ref-type="bibr" rid="ref35">Raj, 1917</xref>; <xref ref-type="bibr" rid="ref11">Chacko and Krishnamurthy, 1948</xref>; <xref ref-type="bibr" rid="ref10">Chacko and Ganapati, 1949</xref>; <xref ref-type="bibr" rid="ref12">Chacko and Krishnamurthy, 1950</xref>; <xref ref-type="bibr" rid="ref9">Chacko, 1954</xref>; <xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>), Chilika lagoon (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>), river Cauvery (<xref ref-type="bibr" rid="ref25">Jones, 1959</xref>; <xref ref-type="bibr" rid="ref43">Swayamprakash, 2014</xref>), and river Krishna (<xref ref-type="bibr" rid="ref25">Jones, 1959</xref>). Although Hilsa was a lucrative fishery in all such riverine resources, the construction of dams and barrages resulted in the decline of Hilsa catch in most of the rivers (<xref rid="SM1" ref-type="supplementary-material">Supplementary material</xref>).</p>
<p>Hilsa fisheries are traditionally open-access in nature. The fisher communities attribute high value to the fish because of its excellent taste and high nutritional value. Hilsa production from inland waters has been reported to be stable during the last two decades, but an increase in marine yields has been observed in the Bay of Bengal regions (<xref ref-type="bibr" rid="ref38">Sajina et al., 2020</xref>). A decline in the catch of Hilsa has been reported in the Hooghly&#x2013;Bhagirathi River system for the last two decades (<xref ref-type="bibr" rid="ref26">Khatua et al., 2020</xref>). The Hilsa fishers of West Bengal undertake Hilsa fishing as their secondary occupation. The production in West Bengal declined from 80,000&#x2009;t to 20,000&#x2009;t over 10&#x2009;years since 2001 (<xref ref-type="bibr" rid="ref37">Sahoo et al., 2018</xref>). Commercial, environmental deterioration and interest-group threats from anthropogenic impacts such as siltation in the estuary mouth of the Hooghly&#x2013;Bhagirathi River system obstructing Hilsa migration into the estuarine system, impact of barrages and dams causing the decline of Hilsa in the upper reaches, juvenile fishing, exploitation of brood fish, lack of compliance with mesh size regulation, ineffective fish passes, loss of habitat with increased water abstraction for irrigation and industrialization, pollution, and climate change have resulted in the decline of Hilsa production in India (<xref ref-type="bibr" rid="ref16">De et al., 1994</xref>, <xref ref-type="bibr" rid="ref17">2001</xref>; <xref ref-type="bibr" rid="ref5">Bhaumik, 2017</xref>; <xref ref-type="bibr" rid="ref37">Sahoo et al., 2018</xref>). The total landing of Hilsa at Farakka declined gradually from 31.8 to 34.4 tonnes during 1994&#x2013;1997 to as low as 6.3&#x2013;6.8 tonnes during 1994&#x2013;1995 to 2000&#x2013;2002 (<xref ref-type="bibr" rid="ref45">Yadav, 2022</xref>).</p>
<p>Hilsa fisheries of West Bengal in India are under the jurisdiction of the State Government of West Bengal (<xref ref-type="bibr" rid="ref3">Bandara and Wijewardene, 2023</xref>). The management measures that have been followed by the State Government are mesh size regulation in the use of gill nets in the way that only 90&#x2013;110&#x2009;mm gill net should be used and that monofilament gill nets below 90&#x2009;mm mesh size and other nets with mesh size below 40&#x2009;mm are banned; Hilsa fishing ban period for 10&#x2009;days in the month of September or October (revolves around 14 September and 24 October depending on lunar cycles) and a general fishing ban on all kinds of fishes in the state from 15 April to 15 June; and mass awareness creation for Hilsa conservation from 2010 onwards. Harvesting, transporting, marketing, and selling Hilsa with less than the body size of 23&#x2009;cm (through bag net, scoop net, lift net, and small meshed gill nets), especially from February to April every year, is illegal in West Bengal. Fishing of Hilsa is prohibited within 5 sq. km of the Farakka barrage around the year to facilitate brooders spawning in the area. The market value of Hilsa is increasing rapidly due to low availability because of overfishing in West Bengal. The commissioning of the Farakka barrage at Murshidabad in the 1970s caused a drastic decline and consequent depletion of the Hilsa population from the upstream of river Ganga, which was once available in plenty up to Allahabad (now known as Prayagraj).</p>
<p>Comprehensive socio-economic studies of Hilsa fishers in India are lacking, and more socio-economic studies in Hilsa fisheries have been encouraged (<xref ref-type="bibr" rid="ref30">Miah, 2015</xref>; <xref rid="SM1" ref-type="supplementary-material">Supplementary material</xref>). Therefore, considering Hilsa as a commercially and culturally important fish but with a significantly declining catch, the socio-economic condition of Hilsa fishermen in river Hooghly of the Ganga River system is deemed essential to analyze the sustainability of Hilsa fisheries. In this background, a hypothesis was developed to examine if the Hilsa fisheries of river Hooghly in the deltaic Ganga region of India are lucrative enough to sustain the livelihood of Hilsa fishers. The objectives were to (i) analyze the sustainability of Hilsa fisheries toward the livelihood of artisanal fishers in the light of the socio-economic conditions of the fishers in river Hooghly and (ii) examine the impact of Farakka barrage on Hilsa fishers along with conservation and management of Hilsa fisheries in West Bengal. Our study was carried out through structured questionnaires by interviewing the Hilsa fishers of river Hooghly in West Bengal with respect to their socio-economic conditions during 2020&#x2013;2021.</p>
</sec>
<sec sec-type="materials|methods" id="sec2">
<label>2</label>
<title>Materials and methods</title>
<sec id="sec3">
<label>2.1</label>
<title>Study area</title>
<p>River Ganga (2,525&#x2009;km) is India&#x2019;s national river and the third largest river in the world. It divides itself into two parts; from Farakka, one part flows to West Bengal as river Hooghly and the other part of Ganga goes to Bangladesh as river Padma. Later, the river Hooghly merges with the Bay of Bengal in the east. Our study was conducted in many villages of the upper stretch of the Hooghly district to its lower stretch (up to almost 300&#x2009;km) in West Bengal during 2020&#x2013;2021. The study areas were divided into four major sampling sites in four districts, which are Farakka in Murshidabad, Hooghly, North 24 Parganas, and South 24 Parganas (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The geographical location of the study area is 22&#x00B0;23&#x2032;40.36&#x2009;N to 24&#x00B0;48&#x2019;53&#x2009;N and 87&#x00B0;55&#x2032;05 E to 88&#x00B0;8&#x2032; 5.27 E.</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Sampling sites of socio-economic survey of Hilsa fishers.</p>
</caption>
<graphic xlink:href="fsufs-08-1310077-g001.tif"/>
</fig>
<p>The landing centers in Hooghly district where surveys were undertaken were Triveni, Ranighat, Baidyabati, Baidyabati Sitaram Bagan, Baidyabati Ranighat, Baidyabati Rajbongshi Para, Srirampur Chhatra Gargari Ghat, Banerjee Lane Srirampur Chhatra, and Bichali Ghat Road. Socio-economic surveys were carried out in the landing centers of North 24 Parganas district, namely Amrika Palli, Kalitala, Garulia, Subhash Nagar Kalyanpalli, Bichali Ghat, Deshbandhu Nagar, Ghoshbagan, Sitalatala, Ichapur, Girish Ghat Road, Dakshinpara, Monirampur Daspara, Jhaugachi Chanditala, R. N. T. Path Titagarh, Titagarh Lakshmi Ghat, B. L. Ghat Road Titagarh, Ruiya Barrackpore, and Kutighat Baranagar. The landing centers of Farakka in Murshidabad district where the surveys were carried out are Hossainpur, Khuntipara, Bindugram, Jafarganj, Nayansukh, Raghunathpur, Panchananelpur, Rajnagar, Hatpara Rajmahal, Barman Colony Rajmahal, Masudan Colony Rajmahal, Dahia tola, Nayatola, Durgasthan, Kamaltola, Bartala, Launchghat, and Bijalighat. Finally, in South 24 Parganas, a socio-economic survey was carried out in Godakhali. A market survey of Hilsa fisheries was also conducted at the Godakhali fish market in South 24 Parganas district to collect gender-disaggregated data from 24 to 25 February 2022.</p>
</sec>
<sec id="sec4">
<label>2.2</label>
<title>Sampling</title>
<p>A total of 402 fishers were surveyed from December 2020 to November 2021 (<xref ref-type="table" rid="tab1">Table 1</xref>). Stratified random sampling was carried out for the study. Sampling was done in four strata (four districts) longitudinally from the middle stretch to the lower stretch of river Hooghly, namely Murshidabad, North 24 Parganas, South 24 Parganas, and Hooghly, as per designated study sites of the National Mission for Clean Ganga Project of ICAR&#x2014;CIFRI. In each district, the households of the Hilsa fishers near the important landing centers were selected randomly. The surveys were based on structured questionnaires, which were pre-tested with a few fishermen in study areas. The questionnaires included questions on fishermen&#x2019;s age, educational status, family size, annual income, daily catch of Hilsa fish, number of boats and nets, type of boat and net, etc. Data were analyzed through descriptive statistical analysis using percentages in MS Office 2010 developed by Microsoft Corporation and a non-parametric test (Kruskal&#x2013;Wallis test) in R-Studio.</p>
<table-wrap position="float" id="tab1">
<label>Table 1</label>
<caption>
<p>Sample size in different sampling stations.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Landing center</th>
<th align="center" valign="top">Fishers fully dependent on fishing</th>
<th align="center" valign="top">Fishers partially dependent on fishing</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Farakka (Murshidabad)</td>
<td align="center" valign="top">84</td>
<td align="center" valign="top">138</td>
</tr>
<tr>
<td align="left" valign="top">North 24 parganas</td>
<td align="center" valign="top">50</td>
<td align="center" valign="top">Nil</td>
</tr>
<tr>
<td align="left" valign="top">South 24 parganas (Godakhali)</td>
<td align="center" valign="top">99</td>
<td align="center" valign="top">17</td>
</tr>
<tr>
<td align="left" valign="top">Hooghly</td>
<td align="center" valign="top">14</td>
<td align="center" valign="top">Nil</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>In this study, two groups of Hilsa fishers, <italic>viz.</italic> Hilsa fishers who are only dependent on Hilsa fishing for their livelihood and Hilsa fishers who have additional employment, are compared to assess if there exist any differences between them with regard to age, education, family members, number of boats, number of nets owned, and income using the Kruskal&#x2013;Wallis H test.</p>
</sec>
</sec>
<sec sec-type="results" id="sec5">
<label>3</label>
<title>Results and discussion</title>
<sec id="sec6">
<label>3.1</label>
<title>Socio-economic conditions of Hilsa fishers of river Hooghly</title>
<sec id="sec7">
<label>3.1.1</label>
<title>Community of Hilsa fishers</title>
<p>The knowledge about communities of Hilsa fishers helps us trace their connection to Hilsa fisheries, whether it was their ancestral occupation or not. The importance of Hilsa fisheries as an integral form of artisanal fishing is well established (<xref ref-type="bibr" rid="ref32">Mome and Arnason, 2008</xref>; <xref ref-type="bibr" rid="ref22">Islam et al., 2016a</xref>,<xref ref-type="bibr" rid="ref23">b</xref>; <xref ref-type="bibr" rid="ref33">Porras et al., 2017</xref>; <xref ref-type="bibr" rid="ref34">Rahman et al., 2020</xref>). Hilsa fishers in all the districts except Murshidabad district (Farakka) entirely belonged to the Scheduled Caste (SC) community and were Hindus in religion. The Hilsa fishers in Farakka were from mixed communities such as SC (88%), General (7%), and OBC (5%, who were Muslim in religion). They are traditional fishers who have been engaged in artisanal Hilsa fisheries to earn their livelihood for generations. Similar finding was obtained about Hilsa fisheries in West Bengal, where 93% of the fishers belonged to SC communities (<xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>). However, the traditional fishers are threatened with losing their artisanal heritage of Hilsa fishing with declining catch, where they are being left with alternatives to opt for non-fishery related wage-earning activities to sustain their livelihood.</p>
</sec>
<sec id="sec8">
<label>3.1.2</label>
<title>Age</title>
<p>In South 24 Parganas district, the dominant age group is 41&#x2013;60&#x2009;years. This implies that the fishers of South 24 Parganas, especially in Godakhali, depend considerably on Hilsa fisheries for their livelihood and for supporting their family. The fishers of Hooghly and Murshidabad (Farakka) districts majorly fall in the age group of 21&#x2013;40&#x2009;years, where the presence of young fishers is evident. This shows that the young family members of fishers&#x2019; families still find Hilsa fisheries as a lucrative option for establishing their livelihood. A similar finding was seen in the Meghna River estuary Hilsa fishers of Bangladesh, with 41% of the fishers in the age group of 26&#x2013;30&#x2009;years and another 38% of the fishers within the age 40&#x2013;60&#x2009;years (<xref ref-type="bibr" rid="ref2">Ahmed et al., 2021</xref>). Another study reported that the average age of Hilsa fishers in Meghna and Padma Hilsa sanctuaries was 35&#x2009;years (<xref ref-type="bibr" rid="ref28">Mahmud, 2020</xref>).</p>
</sec>
<sec id="sec9">
<label>3.1.3</label>
<title>Education</title>
<p>The fishers in the lower stretch of the river Hooghly were comparatively more educated than those in the upper stretch. Most of the Hilsa fishers of Farakka (82%) in the upper stretch of the river Hooghly were illiterate, but in the lower stretch, 65% were educated with at least a primary level of educational attainment. In Murshidabad, only 19% of the fishers fishing in Farakka barrage adjacent area went to school. However, the presence of graduate and post-graduate individuals engaged in fishing was also noticed in Murshidabad and South 24 Parganas districts. Other studies also found that the major educational attainment of Hilsa fishers in West Bengal was only primary school education (<xref ref-type="bibr" rid="ref40">Sinha and Katiha, 2001</xref>; <xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>). It was observed that more Hilsa fishers with secondary occupations in non-fishery activities were educated up to the secondary level of school education in contrast to Hilsa fishers fishing other fishes for their secondary occupation, who were only primary literate. In Bangladesh, the literacy level of Hilsa fishers was also reported to be 40% (<xref ref-type="bibr" rid="ref40">Sinha and Katiha, 2001</xref>).</p>
</sec>
<sec id="sec10">
<label>3.1.4</label>
<title>Family size</title>
<p>The highest average family size was observed in Murshidabad district with five family members in each family and the lowest average with three family members was observed in Godakhali in South 24 Parganas district. Another study in Murshidabad district also found that the average family size of Hilsa fishers is more than 4 (<xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>). The average family size in both Hooghly and North 24 Parganas district was 4. A study in Bangladesh stated that the average family size of Hilsa fishers was 6.2 (<xref ref-type="bibr" rid="ref40">Sinha and Katiha, 2001</xref>).</p>
</sec>
<sec id="sec11">
<label>3.1.5</label>
<title>Occupation</title>
<p>Owing to the dwindling nature of Hilsa fisheries, the fishers in all the study areas depended on avenues other than Hilsa fishing to support their incomes (<xref rid="SM1" ref-type="supplementary-material">Supplementary material</xref>). Hooghly and North 24 Parganas districts&#x2019; fishers depended on fisheries for their livelihood, even during the lean season of Hilsa fishing. They harvested other fish species to supplement their earning from fisheries. However, the fishers of South 24 Parganas and Farakka were more diversified in nature because they depended on non-fishery activities such as mainly working as daily wage laborers and bidi (local cigarette), making for their additional employment. The other minor forms of employment observed were rickshaw drivers, shopkeepers, fruit sellers, tea sellers, nut sellers, and vegetable retailers. However, most of the fishermen had no identity cards, and because of this, they were not getting proper financial support from the government. A study in the Meghna River Estuary of Chandpur, Bangladesh, analyzed that there were significant differences among different groups of Hilsa fishers with varying degrees of dependence on Hilsa fisheries for their livelihood with respect to their age, annual income from fishing, and annual fishing activity days (<xref ref-type="bibr" rid="ref2">Ahmed et al., 2021</xref>).</p>
</sec>
<sec id="sec12">
<label>3.1.6</label>
<title>Dependence on fisheries</title>
<p>In river Hooghly, no Hilsa fishers depend on only Hilsa fisheries for their livelihood. As Hilsa is mainly available in the monsoon (June to August) and winter (October to December) seasons, Hilsa fishing provides only seasonal employment to the fishers. At other times, they are fishing other fish species and other non-fishery daily wage-earning activities. In the lower stretch, especially in Godakhali at South 24 Parganas district, maximum Hilsa fishers worked as part-time laborers on off-seasons; 17.66% of fishers had fishing other species as their secondary occupation. The highest dependence of Hilsa on other fishes to supplement income from Hilsa fisheries was observed in the Hooghly district (56% of Hilsa fishers). The Hilsa fishers (39.44%) of North 24 Parganas district also had considerable dependence on other fisheries to support their secondary occupation. The significant share of other fishery was contributed by prawns (23.88%), Rohu (10.45%), Giant river catfish (<italic>Aristichthys aor</italic>, 10.45%), and Catla (9.7%) (<xref ref-type="fig" rid="fig2">Figure 2</xref>). The other fishes are minor carps such as orangefin labeo (<italic>Labeo calbasu</italic>) and jaya (<italic>Aspidoparia jaya</italic>); catfishes such as snakehead murrel (<italic>Channa striata</italic>), long whiskers catfish (<italic>Mystus gulio</italic>), Giant snakehead (<italic>Channa micropeltes</italic>), rita (<italic>Rita rita</italic>), Climbing perch (<italic>Anabus testudineus</italic>), stinging catfish (<italic>Heteropneustes fossilis</italic>), Gangetic mystus (<italic>Mystus tengra</italic>), freshwater shark (<italic>Wallago attu</italic>), olive barb (<italic>Puntius sarana</italic>), and vacha (<italic>Eutropiichthys vacha</italic>); small indigenous fishes (SIF) such as scribbled goby (<italic>Glossogobius giuris</italic>), chitala (<italic>Chitala chitala</italic>), Ganges river sprat (<italic>Corica soborna</italic>), and bronze featherback (<italic>Notopterus notopterus</italic>); shads (<italic>Gudusia chapra</italic>); and other estuarine fish species such as Gangetic Hairfin Anchovy (<italic>Setipinna phasa</italic>), Asian seabass (<italic>Lates calcarifer</italic>), pama croaker (<italic>Otolithoides pama</italic>), and mango fish (<italic>Polynemus paradesius</italic>) (<xref rid="SM1" ref-type="supplementary-material">Supplementary material</xref>). A previous study observed that few purely freshwater fishes such as <italic>Rita rita, Wallago attu, Mystus aor, Ailia coilia, Catla catla, Labeo rohita,</italic> and <italic>Labeo bata</italic> and prawn (<italic>Macrobrachium rosenbergii</italic>) were observed for the first time in Hooghly estuary in the post-Farakka barrage period after 1975 (<xref ref-type="bibr" rid="ref6">Bhaumik, 2019</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Other fishes caught by Hilsa fishers.</p>
</caption>
<graphic xlink:href="fsufs-08-1310077-g002.tif"/>
</fig>
</sec>
<sec id="sec13">
<label>3.1.7</label>
<title>Fishing assets owned</title>
<p>The major types of boats used for Hilsa fisheries are non-motorized dug-out canoes and boats fitted with outboard motor engines. Fishing operations with engine boats dominated in Murshidabad district (93.7%). Hand boats (dug-out canoes) dominated South 24 Parganas and North 24 Parganas districts. Small-scale mechanization was also said to exist in the nearshore waters of the northern Bay of Bengal (<xref ref-type="bibr" rid="ref14">CMFRI, 2016</xref>) and in the upper stretch through trawlers (<xref ref-type="bibr" rid="ref8">Bhaumik and Sharma, 2011</xref>). Mechanized boats also operate in the marine zone of the Hooghly&#x2013;Bhagirathi estuary within 30&#x2009;km of the estuary mouth during monsoon, which extends up to 60&#x2009;km in the winter. The majority of the fishers own one boat (<xref ref-type="table" rid="tab2">Table 2</xref>). Eight to eleven fishers join a fishing trip in a boat and share the catch among them (<xref ref-type="bibr" rid="ref8">Bhaumik and Sharma, 2011</xref>). Sometimes, a fishing trip of a single boat going out for Hilsa fishing also consisted of two to three persons (<xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>).</p>
<table-wrap position="float" id="tab2">
<label>Table 2</label>
<caption>
<p>Hilsa fishing crafts and gears.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Major sampling site</th>
<th align="left" valign="top">No. of boats owned</th>
<th align="left" valign="top">Boat possession</th>
<th align="left" valign="top">No. of nets in possession</th>
<th align="center" valign="top" colspan="2">Type of Net<sup>&#x002A;</sup></th>
</tr>
<tr>
<th/>
<th/>
<th/>
<th/>
<th align="left" valign="top">Hilsa fishing</th>
<th align="left" valign="top">Other fisheries</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Hooghly district</td>
<td align="left" valign="top">One boat&#x2009;=&#x2009;100%</td>
<td align="left" valign="top">Non-motorized (100%)</td>
<td align="left" valign="top">No own net&#x2009;=&#x2009;29%<break/>One net&#x2009;=&#x2009;31%<break/>Two nets&#x2009;=&#x2009;29%<break/>Three nets&#x2009;=&#x2009;8%<break/>Four nets&#x2009;=&#x2009;2%</td>
<td align="left" valign="top">Gill net possession&#x2009;=&#x2009;100%</td>
<td align="left" valign="top">Drag Net&#x2009;=&#x2009;45.45%<break/>Cast Net&#x2009;=&#x2009;27.27%<break/>Mosquito Net&#x2009;=&#x2009;18.18%<break/>Trawl&#x2009;=&#x2009;9.09%</td>
</tr>
<tr>
<td align="left" valign="top">North 24 Parganas district</td>
<td align="left" valign="top">One boat&#x2009;=&#x2009;91%<break/>Two boats&#x2009;=&#x2009;9%</td>
<td align="left" valign="top">Non-motorized (100%)</td>
<td align="left" valign="top">No own net&#x2009;=&#x2009;45%<break/>One net&#x2009;=&#x2009;27%<break/>Two nets&#x2009;=&#x2009;21%<break/>Three nets&#x2009;=&#x2009;5%<break/>Five nets&#x2009;=&#x2009;1%</td>
<td align="left" valign="top">Gill net possession&#x2009;=&#x2009;98%</td>
<td align="left" valign="top">Bag Net&#x2009;=&#x2009;78.57%<break/>Cast Net&#x2009;=&#x2009;14.29%<break/>Set Barrier&#x2009;=&#x2009;7.14%</td>
</tr>
<tr>
<td align="left" valign="top">Murshidabad district (Farakka)</td>
<td align="left" valign="top">One boat&#x2009;=&#x2009;100%</td>
<td align="left" valign="top">Motorized boat (31%), non-motorized boat (26%), no own boat (42%)</td>
<td align="left" valign="top">No own net&#x2009;=&#x2009;38%<break/>One net&#x2009;=&#x2009;62%</td>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top">South 24 Parganas district</td>
<td align="left" valign="top">One boat&#x2009;=&#x2009;100%</td>
<td align="left" valign="top">Non-motorized boat (61%), Motorized boat (17%), No own boat (22%)</td>
<td align="left" valign="top">No own net&#x2009;=&#x2009;33%<break/>One net&#x2009;=&#x2009;67%</td>
<td/>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><sup>&#x002A;</sup>Hilsa fishing is carried out by gill net only, and the other types of nets are used by fishers when they harvest fish other than Hilsa.</p>
</table-wrap-foot>
</table-wrap>
<p>Gill nets of size 90&#x2013;120&#x2009;mm are generally used by the Hilsa fishers. Drag nets and cast nets are used in catching carps and fish other than Hilsa by the fishers who also harvest other fish in addition to Hilsa. At times, particularly during the monsoon season, the Hilsa fishers also use cast nets and drag nets to catch Hilsa when their sizes are big. Catching Hilsa with a gill net was majorly observed at Farakka in Murshidabad. In Godakhali, in the lower stretch of the river Hooghly, male fishermen were 96.7% catching Hilsa and 3.3% were women Hilsa fishers mainly selling Hilsa in the market.</p>
</sec>
<sec id="sec14">
<label>3.1.8</label>
<title>Income</title>
<p>The average monthly income of Hilsa fishers in the lower stretch (Godakhali in South 24 Parganas, North 24 Parganas district, and Hooghly district) was higher than that in the upper stretch (Farakka in Murshidabad district) (<xref ref-type="fig" rid="fig3">Figure 3</xref>). In Godakhali, the fisher&#x2019;s average monthly income is &#x20B9;25,000&#x2013;30,000 (USD 301&#x2013;361), whereas in the upper stretch, the income is approximately &#x20B9;10,000&#x2013;15,000 (USD 120&#x2013;181) per month. Some studies in the past have reported that the income of individual fishers ranged from &#x20B9;5,000&#x2013;8,000 (USD 60&#x2013;96) per month (<xref ref-type="bibr" rid="ref1">Abdul et al., 2021</xref>). The average monthly income of Hilsa fishers from other fisheries was &#x20B9;2,205 (USD 27) and that from non-fishery activities as secondary occupation was &#x20B9;1,200 (USD 14) (<xref ref-type="table" rid="tab3">Table 3</xref>). A study in Murshidabad district (<xref ref-type="bibr" rid="ref13">Chacraverti, 2021</xref>) stated that the average monthly income of Hilsa fishers during peak season was &#x20B9;9,725 (USD 117) and that in South 24 Parganas was &#x20B9;18,135 (USD 218), and the income of Hilsa fishers during lean seasons ranged from &#x20B9;5,683&#x2013;7,383 (USD 68&#x2013;89).</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Average income (in &#x20B9;1,000) of Hilsa Fishers (percentage of fishers).</p>
</caption>
<graphic xlink:href="fsufs-08-1310077-g003.tif"/>
</fig>
<table-wrap position="float" id="tab3">
<label>Table 3</label>
<caption>
<p>Summary statistics of income of two categories of Hilsa fishers: (i) other fisheries as a secondary occupation and (ii) non-fisheries activities as a secondary occupation.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Parameters</th>
<th align="center" valign="top">Fully dependent on other fisheries for secondary occupation (Average&#x2009;&#x00B1;&#x2009;SD)</th>
<th align="center" valign="top">Dependent on non-fisheries activities for secondary occupation (Average&#x2009;&#x00B1;&#x2009;SD)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Annual income (&#x20B9;1,000) from only Hilsa fisheries</td>
<td align="center" valign="top">90.2&#x2009;&#x00B1;&#x2009;27.37</td>
<td align="center" valign="top">96.99&#x2009;&#x00B1;&#x2009;36.65</td>
</tr>
<tr>
<td align="left" valign="top">Annual income (&#x20B9;1,000) from other sources</td>
<td align="center" valign="top">24.30&#x2009;&#x00B1;&#x2009;5.6</td>
<td align="center" valign="top">14.41&#x2009;&#x00B1;&#x2009;6.18</td>
</tr>
<tr>
<td align="left" valign="top">Total annual income (&#x20B9;1,000)</td>
<td align="center" valign="top">114.51&#x2009;&#x00B1;&#x2009;28.79</td>
<td align="center" valign="top">111.4&#x2009;&#x00B1;&#x2009;38.15</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>There is a significant difference between the two categories of fishers with regard to annual income resulting from Hilsa fisheries and secondary occupations, as shown in <xref ref-type="table" rid="tab4">Table 4</xref>. This points to the fact that more significant income from fisheries is essential for the sustainable management of the fisheries resources of the Hooghly River system. More income from fisheries would attract fishers to venture into Hilsa fishing in peak seasons and other fisheries in the lean seasons. Although Hilsa fisheries are popular as a continued traditional livelihood, it alone is not sufficient enough to support the livelihood of the Hilsa fishers. Therefore, investing in sustainable fisheries management in this area is necessary to facilitate the economic viability of Hilsa fisheries and the sustenance of the traditional livelihood.</p>
<table-wrap position="float" id="tab4">
<label>Table 4</label>
<caption>
<p>Frequency distribution of annual income of two categories of Hilsa fishers: (i) other fisheries as a secondary occupation and (ii) non-fisheries activities as a secondary occupation.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Category</th>
<th align="center" valign="top">&#x003C;&#x20B9;1 Lakh (USD 1205)</th>
<th align="center" valign="top">&#x20B9;1&#x2013;2 Lakhs (USD 1,205&#x2013;2,409)</th>
<th align="center" valign="top">&#x003E;&#x20B9;2 Lakh (USD 2409)</th>
<th align="center" valign="top">Total</th>
<th align="left" valign="top">Chi-square <italic>p</italic>-value</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Fully dependent on Other Fisheries for Secondary Occupation</td>
<td align="center" valign="top">51.25% (82)<sup>&#x002A;</sup></td>
<td align="center" valign="top">35% (56)</td>
<td align="center" valign="top">13.75% (22)</td>
<td align="center" valign="top">100% (160)</td>
<td align="left" valign="top" rowspan="3">0.013 (significant at 5% significance level).</td>
</tr>
<tr>
<td align="left" valign="top">Dependent on Non-Fisheries Activities for Secondary Occupation</td>
<td align="center" valign="top">60.32% (149)</td>
<td align="center" valign="top">34% (84)</td>
<td align="center" valign="top">5.66% (14)</td>
<td align="center" valign="top">100% (247)</td>
</tr>
<tr>
<td align="left" valign="top">Total</td>
<td align="center" valign="top">56.76% (231)</td>
<td align="center" valign="top">34.39% (140)</td>
<td align="center" valign="top">8.85% (36)</td>
<td align="center" valign="top">100% (407)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><sup>&#x002A;</sup>Figures in parentheses denote the number of Hilsa fishers.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec15">
<label>3.1.9</label>
<title>Socio-economic characteristic differences between Hilsa fishers fully dependent on fishing and partially dependent on fishing</title>
<p>The major socio-economic variables such as age, education, income, family size, fishing assets, and occupational structure were analyzed to examine if there exist any differences between Hilsa fishers with other fisheries as their secondary occupation and Hilsa fishers with non-fishery activities as their secondary occupation. The results of the Kruskal&#x2013;Wallis test revealed that there were significant differences with regard to family size, number of boats owned, number of nets owned, annual income and income from secondary occupation at 1% level of significance and income from Hilsa fisheries at 5% level of significance (<xref ref-type="table" rid="tab5">Table 5</xref>). The total annual income of the Hilsa fishers dependent on other fisheries for their secondary occupation was higher than that of the other group. The income earned by Hilsa fishers by harvesting other fish species for their secondary occupation was also significantly higher than that of those with non-fishery activities as their secondary occupation. This testifies to the fact that Hilsa fishers are facing serious challenges in livelihood because of poor and unsustainable catches (<xref ref-type="bibr" rid="ref8">Bhaumik and Sharma, 2011</xref>). A study at the Meghna River estuary of Chandpur in Bangladesh also revealed that the livelihood and living conditions of Hilsa fishers were affected by low literacy levels, lack of professional skills, and low incomes (<xref ref-type="bibr" rid="ref2">Ahmed et al., 2021</xref>). More than two-thirds of the Hilsa fishers there did not have alternative occupations during ban periods.</p>
<table-wrap position="float" id="tab5">
<label>Table 5</label>
<caption>
<p>Kruskal&#x2013;Wallis one-way test between two Hilsa fisher groups.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Parameters</th>
<th align="center" valign="top">Chi-square</th>
<th align="center" valign="top"><italic>p</italic>-value</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="bottom">No. of family members</td>
<td align="center" valign="bottom">10.7031</td>
<td align="center" valign="bottom">0.0011<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="bottom">No. of boats owned</td>
<td align="center" valign="bottom">11.6551</td>
<td align="center" valign="bottom">&#x003C;0.001<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="bottom">No. of nets owned</td>
<td align="center" valign="bottom">43.0845</td>
<td align="center" valign="bottom">&#x003C;0.001<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="bottom">Annual income (K)</td>
<td align="center" valign="bottom">37.5544</td>
<td align="center" valign="bottom">&#x003C;0.001<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="bottom">Income from Hilsa season</td>
<td align="center" valign="bottom">4.4379</td>
<td align="center" valign="bottom">0.0351<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="bottom">Income from secondary occupation</td>
<td align="center" valign="bottom">159.933</td>
<td align="center" valign="bottom">&#x003C;0.001<sup>&#x002A;&#x002A;</sup></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><sup>&#x002A;&#x002A;</sup>Significant at 1% level of significance; <sup>&#x002A;</sup>Significant at 5% level of significance.</p>
</table-wrap-foot>
</table-wrap>
<sec id="sec16">
<label>3.1.9.1</label>
<title>Women in Hilsa fisheries</title>
<p>Godakhali fish market is unique in how women retailers dominate the fish business in the retail fish market. Women fishers in the market have been involved in Hilsa fisheries in the form of their traditional occupation. Their significant involvement is in marketing Hilsa fishes around the landing centers, fishing gear fabrication, and pre-sale processing, such as cleaning and packing to assist their husbands. Out of 20 fish retailers involved in fish marketing in the Godakhali fish market, 80% were female retailers selling Hilsa. Among the male fish retailers, 20% were involved in Hilsa catching, transportation, and fishing gear fabrication apart from the fish business. The fishing gear used are gill nets and bag nets. Apart from Hilsa, the fish retailers also sold Gangetic hairpin anchovy (<italic>Setipinna phasa</italic>), Soldier croaker (<italic>Nibea soldado</italic>), and small prawns, as these species were dominant during the period. The main issues in Hilsa fishery that the women Hilsa fishers narrated are over-fishing, river pollution, and competition between commercial and artisanal fisheries. Even though these issues have become over-arching in the sustainability of Hilsa fisheries, the women vow to support their families in earning their livelihood, supporting the local economy, and passing on traditional knowledge through generations. Women associated with Hilsa fisheries in Bangladesh have been reported to be involved in events such as Hilsa breeding festivals and fisherwomen congress. After women&#x2019;s economic empowerment increased, fishers&#x2019; illegal activities were reduced (<xref ref-type="bibr" rid="ref36">Sahoo et al., 2022</xref>). Studies in Bangladesh have provided varied narratives about women&#x2019;s participation in Hilsa fisheries. In a socio-economic study conducted with the river Meghna Hilsa fishing community at Chandpur, it was stated that women and men are treated equally in terms of their Hilsa fishing rights, even though the extent of their participation varies. Another study in the Meghna estuary Hilsa fisheries of Chandpur stated that women were not allowed large-scale fishing due to social and security problems (<xref ref-type="bibr" rid="ref2">Ahmed et al., 2021</xref>).</p>
</sec>
</sec>
</sec>
<sec id="sec17">
<label>3.2</label>
<title>Impact of Farakka barrage on Hilsa fisheries in river Ganga</title>
<p>The Farakka barrage commissioned in 1971 posed a significant obstacle to Hilsa migration (<xref ref-type="bibr" rid="ref7">Bhaumik and Manna, 2010</xref>). The Farakka barrage has had significant and complex impacts on Hilsa fisheries by altering the river&#x2019;s flow and salinity patterns, affecting Hilsa migration and habitat, and increasing fishing pressure, thereby contributing to the decline of Hilsa fisheries in India. Hilsa fishery collapsed in the stretches of river Ganga above the barrage, with the landings at Allahabad, Buxar, and Bhagalpur drastically dropping to negligible levels (<xref ref-type="bibr" rid="ref42">Swarup, 1958</xref>; <xref ref-type="bibr" rid="ref44">Vass and Moza, 2011</xref>), up to a decline of 92% (<xref ref-type="bibr" rid="ref42">Swarup, 1958</xref>). Therefore, Hilsa now only thrives in the downstream areas of the barrage. Consequently, local fishers stopped providing access to fishing in some stretches of the Ganga after the 1970s. The fishing period also extended throughout the year except for the lean fishing season during the monsoon season. In 2001, the annual net returns of a Hilsa fisher were &#x20B9;29,869 (USD 360), with an average catch of 1431.7&#x2009;kg in the Kanpur to Farakka stretch of the Ganga (<xref ref-type="bibr" rid="ref6">Bhaumik, 2019</xref>). The sale price was &#x20B9;24 (USD 0.3) per kg. Before the construction of the Farakka barrage, the average annual landings of Hilsa varied from 114 to 6,573 tonnes, with an average of 1427.6 tonnes (<xref ref-type="bibr" rid="ref42">Swarup, 1958</xref>).</p>
<p>Hilsa fishery flourished throughout the year in Ganga and its tributaries near Allahabad, with a peak in October and November (<xref ref-type="bibr" rid="ref15">Das et al., 2017</xref>). However, from 1963 to 1972, the Hilsa catch fluctuated between 7.3 tonnes and 113.4 tonnes, with an average of 33 tonnes (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). Again, after the commissioning of the Farakka barrage in 1975, the average annual landing was 0.96 tonnes (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). The aftermath of such scenarios resulted in Hilsa vanishing from the upstream of Ganga above the Farakka barrage. In the Hooghly estuary, the annual Hilsa landing in the pre-Farakka period (1957&#x2013;1974) was 1427.6 tonnes, which increased during the post-barrage period to 6,370 tonnes from 1975 to 1999 (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>; <xref ref-type="bibr" rid="ref6">Bhaumik, 2019</xref>). Hydrological changes such as higher freshwater discharge due to water diversion at the Farakka barrage through the river Hooghly might have attracted more Hilsa toward the Hooghly estuary (<xref ref-type="bibr" rid="ref42">Swarup, 1958</xref>). An important characteristic feature of Hilsa fishery emanated from post-Farakka consequences, which is the winter migratory bag net catches in the lower stretches, resulting in increased catches (<xref ref-type="bibr" rid="ref6">Bhaumik, 2019</xref>).</p>
<p>It was reported that the production of Hilsa in the Hooghly&#x2013;Bhagirathi stretches varied from 12,733 to 77,912 tonnes during 2000&#x2013;2001 to 2010&#x2013;2011 (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). It has also been reported that there is a spurt in Hilsa production every 10 to 12&#x2009;years (<xref ref-type="bibr" rid="ref41">Suresh et al., 2017</xref>). The catch trend of Hilsa off the Hooghly estuary since 2000 indicates a serious decline in the Hooghly River system. In addition, indiscriminate exploitation of Hilsa juveniles through small mesh bags and seine nets was reported during 1991&#x2013;1998 and 1998&#x2013;2003. On the other hand, the post-Farakka period has seen an increase in the catch of Hilsa, which peaked in 2004&#x2013;2005 at 8427&#x2009;t. The building of the Farakka barrage created a barrier for Hilsa migration upstream, which is why the trend of Hilsa catch at the Hooghly estuary has been rising. The barrage has had a devastating impact on Hilsa breeding due to obstruction in its migration.</p>
<p>India and Bangladesh have also experienced tension due to the Farakka Barrage. Conflicts over water sharing and its effects on Hilsa fisheries have arisen due to the changing river flow, which influenced fisheries in both countries. These issues have had geopolitical and diplomatic ramifications. The socio-economic interviews of our study also revealed some interesting findings in areas upwards of the Farakka barrage. In Jharkhand, young fishers were unable to recognize the Hilsa shown to them in pictures, in contrast to the elderly fishers (above 65 to 70&#x2009;years) who knew about the identifying characteristics of the fish. Under the umbrella of the National Mission for Clean Ganga (NMCG), an authority under the Ministry of Jal Shakti, Government of India, ICAR-CIFRI, has been making efforts to increase the Hilsa population in the upstream of Farakka barrage since March 2017. From March to June 2017, the Hilsa catch was estimated as 1,315&#x2009;kg in downstream and 736&#x2009;kg in the feeder canal. Hilsa catch in the upper stretch and navigational channel was represented by juveniles but negligible in quantity. This finding is unique and indicates the possibilities of breeding and spawning Hilsa in the vicinity of the Farakka barrage. This pointed to the fact that recruitment of Hilsa fishery is dependent on smaller age groups due to the absence of higher age group fishes in and around the Farakka barrage (<xref ref-type="bibr" rid="ref15">Das et al., 2017</xref>).</p>
</sec>
</sec>
<sec sec-type="conclusions" id="sec18">
<label>4</label>
<title>Conclusion</title>
<p>Hilsa fishers of river Hooghly have been vulnerable to commercial threats (creation of dams and barrages and developmental activities), environmental deterioration threats (deterioration of habitat and pollution), and interest group threats (indiscriminate juvenile catching, overexploitation, non-compliance with regulatory measures, and use of small mesh sized fishing gears), resulting into declining production, uncertain income, and occupational shift. Although Hilsa fish have enormous socio-economic and cultural significance for the Bengali community, the traditional Hilsa fishers no longer depend solely on Hilsa fisheries for livelihood but look forward to other fisheries to secure higher income. The sustainability of the artisanal Hilsa fisheries needs to be looked into to support the livelihood of the fishers. The Farakka barrage commissioned in 1971 altered river Ganga&#x2019;s flow and salinity patterns, affecting Hilsa migration and causing a remarkable decline in Hilsa catch in the upper stretches of Ganga. This has created pressure on the fishery resource, for which recent initiatives have been taken to increase the Hilsa population upstream of the Farakka barrage. The fact that Hilsa was once available in the different river systems of the country and then suffered huge setbacks owing to the construction of dams and barrages needs to be considered in the management and policy decisions for the sustenance and development of Hilsa fisheries. From the study, the occupational shift was observed where traditional Hilsa fishers have shifted to non-fishery activities such as rickshaw driving, shopkeeping, fruit selling, tea shop, nut selling, and vegetable retailing. Since Hilsa fishing is a family business, more involvement of women would be profitable. The management and conservation rules pertaining to Hilsa fisheries policies have to be strictly implemented and monitored through mesh size regulation of gill net, Hilsa fishing ban period (for 10&#x2009;days in September or October depending on lunar cycles), ban of juvenile catching of Hilsa with body size less than 23&#x2009;cm, and prohibition of Hilsa fishing within 5 sq. km of the Farakka barrage round the year. Considering the high market demand for Hilsa in the eastern and north-eastern regions of India and the market complexities, more significant investments need to be channeled into the Hilsa fisheries of the northern Bay of Bengal region. Such investments encompass a wholesome approach, including more governmental initiatives for conservation and management. The study provides scope for an enhanced understanding of the factors that would drive the revival of Hilsa fisheries in river Hooghly and supplement the livelihood of fishers in the deltaic Ganga region.</p>
</sec>
<sec sec-type="data-availability" id="sec19">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, upon request.</p>
</sec>
<sec sec-type="ethics-statement" id="sec20">
<title>Ethics statement</title>
<p>The experiment conducted in the present study has been passed through the institute&#x2019;s ethical committee, and the committee approved the carry out the experiment sampling of fish and its handling were performed as per the instruction laid by the ethical committee.</p>
</sec>
<sec sec-type="author-contributions" id="sec21">
<title>Author contributions</title>
<p>HC: Conceptualization, Data curation, Investigation, Methodology, Software, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing, Formal analysis. PD: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Software, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. AK: Investigation, Writing &#x2013; review &#x0026; editing. SN: Investigation, Writing &#x2013; review &#x0026; editing. CJ: Conceptualization, Data curation, Formal analysis, Methodology, Software, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. AS: Conceptualization, Formal analysis, Methodology, Supervision, Writing &#x2013; review &#x0026; editing. BD: Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Project administration, Resources, Software, Supervision, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing.</p>
</sec>
</body>
<back>
<sec sec-type="funding-information" id="sec22">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. Funding for this research study was obtained from externally funded project National Mission for Clean Ganga at ICAR - CIFRI. Grant No. Ad-35012/1/2023-NMCG-NMCG.</p>
</sec>
<ack>
<p>The authors would like to acknowledge the Director and Scientists of the ICAR - Central Inland Fisheries Research Institute, Barrackpore, Kolkata, India, and the NMCG for their financial and technical support during the tour programs and the supportive members who helped us during the interview session of the fishermen. The authors also would like to acknowledge the Indian Hilsa fishermen for their cooperation.</p>
</ack>
<sec sec-type="COI-statement" id="sec23">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="sec100" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec sec-type="supplementary-material" id="sec24">
<title>Supplementary material</title>
<p>The Supplementary material for this article can be found online at: <ext-link xlink:href="https://www.frontiersin.org/articles/10.3389/fsufs.2024.1310077/full#supplementary-material" ext-link-type="uri">https://www.frontiersin.org/articles/10.3389/fsufs.2024.1310077/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Data_Sheet_1.PDF" id="SM1" mimetype="application/pdf" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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