The present study is based on the finfish catch and bycatch data collected from the commercial trawlers operated along the coast of Nagapattinam from January 2017 to August 2019.
Estimated annual landings and finfish bycatch of trawl fishery
The estimated annual average landing of trawl catch was 15,414.41 tonnes with an annual average fishing effort of 9,327 boat-days. In the annual average landings, commercial catch shared 70.75% (10,905.78 tonnes) and annual finfish bycatch formed 21.12% (3,256.14 tonnes). Furthermore, juveniles of finfish constituted 56.88% (1851.94 tonnes) of the annual bycatch landing. The peak fishing effort was observed in March 2017 (1975) followed by March 2019 (1694), March 2018 (1660) and it was observed to be the lowest in February 2018 (140), followed by September 2018 (192), September 2017 (207) with the fishing effort ranging from 140 (February 2018) to 1975 boat-days (March 2017) during the study period (Table 1) and monthwise estimated landing of total catch, commercial catch, finfish bycatch and low value juvenile finfish bycatch are illustrated in Fig 2.
Taxonomical identification of finfish bycatch
Along the coast of Nagapattinam, 210 species of finfishes belonging to 15 orders, 79 families and 153 genera were collected from the bycatch of trawl fishing from January 2017 to August 2019. Finfish order-wise contribution of bycatch along the Nagapattinam region are showed in Fig 3. Additionally, 12 species of deep-sea fishes such as
Neoharriotta pinnata,
Harpadon nehereus,
Hoplostethus mediterraneus,
Psenopsis cyanea,
Neoepinnula orientalis,
Lepidocybium flavobrunneum,
Sphagemacrurus pumiliceps,
Physiculus roseus,
Alepocephalus bicolor,
Lophiodes mutilus, Chascanopsetta lugubris and
Ectreposebastes imus and 9 finfish species of rare groups including
Mola mola, Bregmaceros mcclellandi, Atherinomorus lacunosus, Ptarmus jubatus, Satyrichthys laticeps, Pterygotrigla hemisticta, Opistognathus nigromarginatus, Bleekeria kallolepis and
Bleekeria murtii were also recorded.
Univariate analysis of monthly diversity
Monthly values of species richness (S) was recorded maximum during September 2017 (134) and minimum during June 2018 (53) and Margalef’s Species richness (d) value was recorded high in September 2017 (19.25) and low in June 2018 (8.18). The Species richness and diversity are indicative of the stability of a community, (2014). Shannon-Wiener’s diversity index (H’) was the highest in September 2017 (6.5479) and the lowest in June 2018 (4.9144). The range of the indices in the trawl fishing indicated the diverse nature of bycatch finfish species. Shannon Weiner Index (H’) value was estimated to be low during June which may be due to the non-operation of trawlers due to trawl ban enforced between between 15
th April and 14
th June. During the study period, the H’ value was found to be low during December 2017 (5.2870), followed by June 2018 (4.9144), January 2019 (5.2043) which may be due to the dominance of one or few finfish species (Clupeid group during December 2017, Leiognathid group during June 2018, grunters and Leiognathid groups during January 2019). Similar H’ values of trawl finfish bycatch ranging from 5.6266 to 4.5265 (
Kodeeswaran, 2019) and crustacean bycatch from 5.53 to 3.13 (
Pillai, 2014) were reported along the Chennai Coast. Species evenness (J') value was found to be high in September 2018 (0.939) and low in June 2019 (0.852), revealing that finfish species were evenly distributed over the months and there was not much difference in the species distribution along the coast of Nagapattinam. It is a well-known fact that the species diversity is found maximum if all species are equally abundant in the community. The Species richness (d) was found to be high in September 2017 (19.25) and low in June 2018 (8.18), giving an idea of variation in the species richness between different months during 2017-2019 in Nagapattinam coast. The species richness and evenness might be high and low in certain months which may be due to the migration of fish species influenced by the water temperature. When water temperature increases there is a coincidental increase in plankton biomass resulting in a high diversity level (
Pillai, 2014). The monthly taxonomic diversity (∆) was recorded high in August 2018 (92.99), followed by September 2017 (91.39) and low in June 2018 (77.86). The monthly total phylogenetic diversity was observed high in September 2017 (7425) and low in June 2018 (3175). The values of taxonomic diversity and phylogenetic diversity are supportive and useful to understand the monthly diversity of finfish bycatch. The univariate analysis of monthly diversity is tabulated in Table 2.
Multivariate analysis of monthly diversity
The multivariate analysis performed through cluster analysis revealed the similarity in finfish bycatch diversity between months and seasons. Like-wise, the K-dominance plot was drawn used to illustrate the abundance of different finfish bycatch species in different months and seasons during the study period. The cluster analysis of trawl finfish by catch showed the highest similarity (66.68%) between September 2018 and September 2017 and the lowest similarity (30.21%) between February 2019 and June 2018. The results of cluster analysis showed the presence of finfish species over different months (Fig 4). The study revealed that finfish bycatch landed in the trawl fishery of Nagapattinam coast are diverse in nature (6.5479-4.9144) and species assemblages are in a parallel manner across the months. The abundant diversity of bycatch species is a common phenomenon in trawler fisheries ((
Pillai, 2014);
Saila, 1983).
The K-dominance curve was obtained by plotting percentage cumulative abundance against species rank (K) on a logarithmic scale and the curve provides an undisturbed ecosystem exposed with an S-shaped curve. In the Nagapattinam coast, the plot showed that the curve for September 2017 and November 2018, which lie on the lower side, extended further and rose slowly due to the high intensity of species in this month. The dominance plot showed that the density of finfish bycatch species was high in September 2017 and November 2018 and proved that the number of species (richness) was more when compared to other months (Fig 5). Similar findings of abundant high diversity were observed along Chennai coast in December
(Kodeeswaran, 2019), Thoothukudi coast in September (
Ranjith, 2015) and Mangalore coast in October
(Kumar et al., 2015; Sonwal et al., 2019).
Univariate analysis of seasonal diversity
A year was divided into four seasons namely summer (April, May, June), pre-monsoon (July, August, September), monsoon (October, November, December) and post-monsoon months (January, February, March) to assess the seasonal diversity (
Pillai, 2014). Season-wise univariate analysis revealed that the species richness (S) ranged from 183 (monsoon 2017) to 123 (post-monsoon 2017) and Margalef’s species richness (d) value ranged from 23.3575 (monsoon 2017) to 17.4877 (post-monsoon 2017). Similarly, species evenness (J') ranged from 0.9266 (monsoon 2018) to 0.8434 (premonsoon 2019). The estimated Shannon - Weiner index was found to be within the range of 6.9241 (post-monsoon 2017) - 6.0386 (premonsoon 2019) whereas, taxonomic diversity (∆) ranged from 90.92 (summer 2018) to 84.38 (post-monsoon 2019) and phylogenetic index ranged from 9775 (monsoon 2017) to 7025 (post-monsoon 2017). Upon comparing the different seasons of the study period, the monsoon seasons showed the maximum diversity (Table 3).
Multivariate analysis of seasonal diversity
The dendrogram of cluster analysis showed higher similarity (80.62%) between postmonsoon seasons of 2017 and 2018 and lower similarity (49.21%) between summer 2018 and monsoon 2019 (Fig 6). The seasonal K dominance curve indicated the high density of species during premonsoon 2017 and monsoon 2018 (Fig 7). In the present study, the highest seasonal similarity was found during post-monsoon, indicating that there was good recruitment to the fishery immediately after the monsoon season along the coast of Nagapattinam. The similarity findings of Nagapattinam region in the present study were in conformity with the findings of
Kodeeswaran (2019),
Purusothaman et al. (2016),
Kumar et al. (2015),
Ranjith (2015),
Karuppasamy et al. (2020) and
Saroj et al. (2020). Additionally, high species abundance was reported in the premonsoon season which could be attributed to the trawl ban season.