INFLUENCE OF ENVIRONMENTAL PARAMETERS ON FISHERY

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Chapter 5 INFLUENCE OF ENVIRONMENTAL PARAMETERS ON FISHERY 5. Introduction Environmental factors contribute to the population dynamics and abundance of marine fishery. The relationships between weather, ocean conditions and the fish behaviour, result in the variability of fish catch. These relationships need not necessarily be always direct. The fish search for and select a certain optimum combination of physical and biological conditions in the environment. Temperature is a major factor for analysing the fish occurrence and behaviour. It is not only a factor for analysing the fish, but it indicates indirectly several other processes in the ocean such as mixing, currents, upwelling etc, all of which affect fishery resources. Many fishes respond to currents, their convergences, divergences and large scale eddies, which result in upwelling/downwelling. For getting the complete understanding of the complex interactions between fishery and its affecting factors, a much closer collaboration between the physical, biological and statistical economic sciences is needed. The relation between the fish and its environment is complex indeed. Influence of physical processes on temporal fluctuations in landings has been studied by Longhurst and Wooster (99), Lluch-Cota et al. (999) and Madhupratap et al. (a). There are some studies which relate fishery and climate factors such as precipitation, temperature (Murty and Edelman, 97; Lluch-Belda et al., 99; Xu and Li, b; Joseph and Jayaprakash, 3; Norton and Mason, 5; Suda et al., 5), human exploitation 3 3

Chapter-5 (Myers et al., 996; Cook et al., 997) or biotic factors including densitydependent survival and growth due to competition (Sundby et al., 989; Myers and Cadigan, 993; Stenseth et al., 999; Lorenzen and Enberg, ; Xu and Li, a). This chapter summarizes briefly some of the effects of environment on the landings of oil sardine and mackerel during 99-8. The correlation between these species and environmental parameters along the coastal waters of southwest coast of India are established here. The more relevant parameters which influence the fishery are sorted out. The impact of IOD on oil sardine and mackerel landings has also been established. 5. Data & Methods Oil sardine and mackerel ladings data are used to establish the correlation with environmental parameters. From the quarterly data sets the annual data from July to next June has been taken (the third and fourth quarters of the corresponding year and first and second quarters of next year) to represent the fishery which starts after every summer monsoon season. The seasonal landings data from October to March (fourth and first quarter) also are used for the correlation study as it represents the period of maximum catch as well as the period of peak IOD events. Environmental information corresponds to two different geographic scales: regional data including summer monsoon rainfall and upwelling index and large-scale indices such as DMI and Nino 3.4 index. Additionally the oceanographic parameters such as SST, SSS and SSH were used to establish a relationship between fishery and environment. The sources of all the environmental parameters are explained in the third chapter. The oceanographic data has been averaged over 74-78 E and 8-5 N (coastal waters of southwest coast of India). 4

The statistical analyses have been done with SPSS (Ver. 5.). To examine the possible relationship between fishery and the environment, the correlations are worked out between time series of fish landings and averages of environmental variables of that region for a time period of October to March. The upwelling index from LTA has been taken as an average from June to September (summer monsoon). SMR of Kerala and Coastal Karnataka has been added together for correlating with fish landings of the southwest coast. The fishery response due to the changes in environmental factors is analyzed with the regression analysis. Since all the environmental parameters are closely interlinked, the multiple regression analysis on these parameters altogether is not possible. Hence the linear regression analysis method has been preferred in this study. Linear regression typically uses the least squares method to determine which line best fits the data (Bowerman et al., 5). R is a measure of how well the data points match the resulting line. 5.3 Results & Discussion 5.3. Influence of environmental parameters on Oil Sardine fishery Figure 5. and figure 5. represent the interannual variability of oil sardine landings with respect to the above mentioned environmental parameters. From these figures it is clear that oil sardine has a negative correlation with SSH and SMR and a positive correlation with SST, SSS and Upwelling Index (UI). The increase in the magnitude of positive DMI during the study period shows a decrease in oil sardine landings. Since the increase in DMI represents the positive IOD years where there is a hike in SSH during fall and winter monsoon months and deepening of MLD. This MLD variation can be considered as the reason for the decrease in oil sardine landing during this period. Fishes are highly migratory with respect to the deepening and shoaling of MLD. During the positive IOD years the coastal waters of 5 5

Chapter-5 southwest coast of India the upwelling intensity during summer monsoon months is less (explained in section 3.3..7) as compared to the other years. Also the rainfall is more in positive IOD years which affect the fishery in its larval stage. During intensive rainfall, the eggs and larvae of oil sardine are getting washed out. The low primary production in this area during the positive IOD years inversely affects the fish population in that region. SST and SSS also show a direct relationship with the oil sardine fishery. The increase in the magnitude of negative DMI during the study period shows an increase in oil sardine landings. In negative IOD years during the fall and winter monsoon months, there is a lowering of SSH and cause shoaling of MLD. During the summer monsoon months of negative IOD years the upwelling intensity is more and cause maximum primary production. These conditions favored a good fishery during these years. The correlation (Pearson) coefficients between environmental parameters and oil sardine fishery are shown in Table 5.. The relation between oil sardine landings and the environmental parameters can be represented by scatter plots. Results of linear regression analysis between oil sardine landings and the environmental parameters which have significant correlation coefficient are shown in Table 5.. The R obtained for oil sardine landings with different environmental parameters (SST, SSS, UI, SSH and SMR) are shown in figure 5.3. All the positive correlations are aligned in the left panel and the negative correlations are in right panel. SST, SSS and UI show positive correlation with oil sardine landings and negative correlation with SSH and SMR. Among which SSH shows a maximum correlation (R =.765) with oil sardine fishery. As SSH increases the MLD deepens and which badly affect the oil sardine fishery. 6

45 4 35 3 5 5 5 Dipole Mode Index Nino 3.4 index 999- - - -3 3-4 4-5 5-6 6-7 7-8 Oil sardine (Jul-Jun) 45 4 35 3 5 5 5 3..5..5..5. -.5 -. -.5 -. -.5 6 55 5 45 4 35 3 36 35.8 35.6 35.4 35. 35 34.8 34.6 34.4 34. 34 Summer Monsoon Rainfall (cm) Oil sardine (Jul-Jun) Summer Monsoon Rainfall 999- - - -3 3-4 4-5 5-6 6-7 7-8 Nino 3.4 Index Upwelling Index DMI - - - Upwelling Index _LTA Oil sardine (Jul-Jun) Oil sardine (Jul-Jun) 999- - - -3 3-4 4-5 5-6 6-7 7-8 45 4 35 3 5 5 5 Oil sardine (IV&I Quarter) Sea Surface Salinity (Oct-Mar) 7 7 Sea Surface Salinity (psu) 999- - - -3 3-4 4-5 5-6 6-7 7-8.8.7.6.5.4.3... 3 5 5 5 4. 4. 4. 39. 38. 37. 36. 35. Sea Surface Height (cm) 999- - - -3 3-4 4-5 5-6 6-7 7-8 45 4 35 3 5 5 5 Oil sardine (IV&I Quarter) Sea Surface Temperature (Oct-Mar) 3 9.5 9 8.5 8 7.5 7 Sea Surface Temperature (C) Fig. 5.: Interannual variability of oil sardine landings with DMI, Nino3.4 Index, UI and SMR 3 5 5 Oil sardine (IV&I Quarter) Sea Surface Height (Oct-Mar) 999- - - -3 3-4 4-5 5-6 6-7 7-8 5 3 5 5 5 Fig. 5.: Interannual variability of oil sardine landings with SST, SSS and SSH 999- - - -3 3-4 4-5 5-6 6-7 7-8

Chapter-5 (a) (d) (b) (e) (c) Fig. 5.3: Scatter plot between oil sardine landings and (a) SST (b) SSS (c) UI (d) SSH (e) SMR 8

Table 5.: Correlation coefficients between Oil Sardine landings and environmental parameters Pearson Correlation Coefficients Oil Sardine current year Oil Sardine next (Jul-Jun) year(jul-jun).358.45 Oil Sardine (Oct-Mar).357 Variables SST SSS.665**.559*.44 UI.657**.74**.75** SSH -.765** -.79** -.69* SMR -.64** -.76** -.579* ** Correlation is significant at the. level (-tailed) * Correlation is significant at the.5 level (-tailed) Table 5.: Regression analysis of Oil Sardine landings and environmental parameters Dependent Variable Independent Variable Unstandardized Coefficients Beta t Sig. R B Std. error 78495.8 57..665 3.45.4.443-578.4 79.7 -.765-4.44..585 UI 58.6 368..74 3.953..5 SWR -495. 4.7 -.76-3.73..499 UI 537958.9 69.9.75 4.66..565 SWR -78.5 48.7 -.579 -.66.9.336 SSS Oil Sardine (Oct-Mar) (Oct-Mar) SSH (Oct-Mar) Oil Sardine Current (Jul-Jun) Oil Sardine Next (Jul-Jun) NB: B : Beta : R : These are the values for the regression equation for predicting the dependent variable from the independent variable These are the standardized coefficients t & Sig. : These are the t-statistics and their associated -tailed p-values used in testing whether a given coefficient is significantly different from zero. The smaller the value of Sig. (and the larger the value of t) the greater the contribution of that predictor These are the proportions of variance in the dependent variable which can be explained by the independent variables 9 9

Chapter-5 5.3. Influence of environmental parameters on Mackerel fishery Figure 5.4 and figure 5.5 represent the interannual variation of the mackerel landings with the environmental parameters. Mackerel shows a negative correlation with SST, SSS and UI and a positive correlation with SSH and SMR. The correlation (Pearson) coefficients between environmental parameters and mackerel fishery are shown in Table 5.3. Results of linear regression analysis performed for mackerel landings and the environmental parameters do not show any significant relation. The R obtained for mackerel landings with different environmental parameters (SST, SSS, UI, SSH and SMR) are shown in figure 5.6. All the negative correlations are aligned in the left panel and the positive correlations are in right panel. So it can be concluded that mackerel fishery is more adaptive to the changes in these parameters as compared to the oil sardine fishery. Table 5.3: Correlation coefficients between Mackerel landings and environmental parameters Variables SST Pearson Correlation Coefficients Mackerel Mackerel Mackerel current year next year (Oct-Mar) (Jul-Jun) (Jul-Jun) -.8 -.85 -.68 SSS -.85 -.35 -.7 SSH.55.47.94 UI -.88 -.49 -.56 SMR.6.3.45 ** Correlation is significant at the. level (-tailed) * Correlation is significant at the.5 level (-tailed) 3

Mackerel Landings Mackerel Landings Mackerel Landings 5 5 5 DMI - - -.8.7.6.5.4.3... Upwelling Index _LTA 999- - - -3 3-4 4-5 5-6 6-7 7-8 Mackerel (Jul-Jun) Mackerel (Jul-Jun) 5 5 999- - - -3 3-4 4-5 5-6 6-7 7-8 Dipole Mode Index Upwelling Index Mackerel Landings 5 5 Mackerel (Jul-Jun) Mackerel (Jul-Jun) 999- - - -3 3-4 4-5 5-6 6-7 7-8 Nino 3.4 index Summer Monsoon Rainfall 3..5..5..5. -.5 -. -.5 -. -.5 6 55 5 45 4 35 3 36 35.8 35.6 35.4 35. 35 34.8 34.6 34.4 34. 34 Summer Monsoon Rainfall (cm) 5 5 5 5 999- - - -3 3-4 4-5 5-6 6-7 7-8 Nino 3.4 Index Mackerel Landings Mackerel (IV&I Quarter) Sea Surface Salinity (Oct-Mar) 3 3 Sea Surface Salinity (psu) 8 6 4 4. 4. 4. 39. 38. 37. 36. 35. Sea Surface Height (cm) 999- - - -3 3-4 4-5 5-6 6-7 7-8 5 3 Mackerel Landings Mackerel (IV&I Quarter) Sea Surface Temperature (Oct-Mar) 9.5 9 8.5 8 Sea Surface Temperature (C) Fig. 5.4: Variability of Mackerel landings with DMI, Nino 3.4 index, UI and SMR 8 6 7.5 7 Mackerel (IV&I Quarter) Sea Surface Height (Oct-Mar) 999- - - -3 3-4 4-5 5-6 6-7 7-8 4 Ye ar 8 6 4 Fig. 5.5: Variability of Mackerel landings with SST, SSS and SSH 999- - - -3 3-4 4-5 5-6 6-7 7-8

Chapter-5 (a) (d) (b) (e) (c) Fig. 5.6: Scatter plot between Mackerel landings and (a) SST (b) SSS(c) UI (d) SSH (e) SMR 3

5.3.3 Prediction with environmental parameters The prediction of oil sardine landings has been attempted with the environmental parameters, which shows significant relation with oil sardine landings. Here SSH, UI, SMR and SSS are taken as the significant environmental parameters. Since all the selected parameters are interconnected, it is impossible to predict the oil sardine landings by taking all these parameters together. Hence the analysis has been done independently for all these parameters. Fig. 5.7: Scatterplot of the observed landings of oil sardine against the predicted landings; from (a) SSH (b) UI (c) SMR (d) SSS Figure 5.7 shows the relationship between the observed and predicted oil sardine landings. The predicted values and the observations are significantly correlated. The most significant values are from SSH (R = 33 33

Chapter-5.79). Therefore, SSH plays a major role in the variations of annual landings of oil sardine along southwest coast of India. The other parameters such as UI, SMR and SSS also show some roles in the variations in annual oil sardine landings. So it can be concluded that these parameters can be accepted for future prediction of the oil sardine fishery. At the same time this prediction method is not applicable to the mackerel fishery. 5.4 Conclusion During the positive IOD years the oil sardine landings show drastic changes compared to normal years. The increase in the magnitude of positive DMI shows a decrease in oil sardine landings of southwest coast of India. The landings exhibit a negative correlation with SSH and SMR and a positive correlation with SST, SSS and UI. Fishes are highly migratory with respect to the deepening and shoaling of MLD. The MLD deepening associated with positive IOD years can be considered as one of the reasons for the decrease in oil sardine landings. During the positive IOD years the coastal waters of southwest coast of India shows a less upwelling intensity during summer monsoon months as compared to the other years. The intensive rainfall associated with the positive IOD years affect the oil sardine fishery in its larval stage. The low primary production in this area during the positive IOD years inversely affects the fish population in that region. SST and SSS also show a direct relationship with the oil sardine fishery. The increase in the magnitude of negative DMI shows an increase in oil sardine landings. In negative IOD years during the fall and winter monsoon months, there is a lowering of SSH and cause shoaling of MLD. During the summer monsoon months of negative IOD years the upwelling intensity is more and cause maximum primary production. These conditions favored a good oil sardine fishery during these years. 34

From the analysis, it can be seen that SST, SSS and UI show positive correlation with oil sardine landings and negative correlation with SSH and SMR. SSH shows a maximum correlation (R = -.765) with oil sardine fishery. The mackerel landings and the environmental parameters do not show any significant relation. SSH plays a major role in the variations of annual landings of oil sardine along southwest coast of India. The other parameters such as UI, SMR and SSS also show some roles in the variations in annual oil sardine landings. So it can be concluded that these environmental parameters can be well accepted for the prediction of the oil sardine fishery. In contrary, this prediction method is not applicable to the mackerel fishery...xy.. 35 35