Abstract

Forecasting, using time series data, has become the most relevant and effective tool for fisheries stock assessment. Autoregressive integrated moving average (ARIMA) modeling has been commonly used to predict the general trend for fish landings with increased reliability and precision. In this paper, ARIMA models were applied to predict Lake Malombe annual fish landings and catch per unit effort (CPUE). The annual fish landings and CPUE trends were first observed and both were non-stationary. The first-order differencing was applied to transform the non-stationary data into stationary. Autocorrelation functions (AC), partial autocorrelation function (PAC), Akaike information criterion (AIC), Bayesian information criterion (BIC), square root of the mean square error (RMSE), the mean absolute error (MAE), percentage standard error of prediction (SEP), average relative variance (ARV), Gaussian maximum likelihood estimation (GMLE) algorithm, efficiency coefficient (E2), coefficient of determination (R2), and persistent index (PI) were estimated, which led to the identification and construction of ARIMA models, suitable in explaining the time series and forecasting. According to the measures of forecasting accuracy, the best forecasting models for fish landings and CPUE were ARIMA (0,1,1) and ARIMA (0,1,0). These models had the lowest values AIC, BIC, RMSE, MAE, SEP, ARV. The models further displayed the highest values of GMLE, PI, R2, and E2. The “auto. arima ()” command in R version 3.6.3 further displayed ARIMA (0,1,1) and ARIMA (0,1,0) as the best. The selected models satisfactorily forecasted the fish landings of 2725.243 metric tons and CPUE of 0.097 kg/h by 2024.

Highlights

  • Lake Malombe is located within the Upper and Middle Shire River basin in the Southern part of Malawi

  • Modeling and forecasting of fish landings and catch per unit effort (CPUE) were conducted based on the raw data

  • The same observation is made in the catch per unit effort (CPUE) data plot which shows the highest within the period from 1976 to 1980

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Summary

Introduction

The above evidence impelled the Malawi government to take a command control approach (stipulated in the guideline of Fisheries Act [3] formulated based on the Laws of Malawi, Chapter 66:05 1974 and amended in 1976, 1977, 1979, 1984, 1996, and 1997, which include gear licensing, gear and mesh size regulations, implementation of the closed season, banning of fine-meshed beach seines and regulating fishing effort) to reverse the situation. This approach faced strong resistance in its implementation and failed to achieve its objective. It was further argued that the implementation arrangements of this approach followed the top-down method, was donor-driven, not formed within a new institutional vacuum, and did not take into account the institutional landscape and diversity that impacted the functioning and performance of the structures [6]

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