FCRR
Spatial Simulations of Hong Kong's Marine Ecosystem: Ecological and Economic Forecasting of Marine Protected Areas With Human-Made Reefs
Editors
Publication
2002 | PDF
Edited by Pitcher, T., Buchary, E. and Trujillo, P.
ABSTRACT
The Hong Kong Agriculture, Fisheries and Conservation Department (AFCD) has initiated a $HK100 million Artificial Reef and Fishery Protected Area (AR/FPA) programme (Figure 1.1). The proposal builds on earlier initiatives to establish ARs in Hoi Ha Wan and Yat Chau Tong Marine Parks. The objective is to rebuild fish stocks by compensating for habitat loss and reducing fishing pressure. An extensive consultation process conducted by ERM-HK Ltd., under contract to AFCD, identified five priority deployment areas. The University of British Columbia Fisheries Centre (UBC-FC) advised on Phase I consultations with fishing communities and conducted extensive ecosystem (ECOPATH and ECOSIM) and bio-economic modelling to determine the effectiveness of different sizes of FPAs around AR complexes. The earlier results indicated that a potential for substantial gains in the value of Hong Kong fisheries resources. This study is the first application of spatial (ECOSPACE) modelling to Hong Kong and adjacent PRC inshore waters and evaluates the effectiveness of different FPA configurations in the Tap Mun/Tolo Harbour and Outer Port Shelter FPAs shown below. The overall modelling also evaluates the benefits of recent AR/FPA initiatives in banning trawling at FPAs, Marine Parks and at the newly established Marine Exclusion Zone at Chek Lap Kok. Lastly, the study assesses the implication of a 2-month trawl moratorium in adjacent PRC inshore waters.
STUDY OBJECTIVES
- Quantify the contribution of ARs plus Fisheries Protection Areas (FPAs) to Hong Kong fisheries resources; and
- Quantify the benefits of banning trawling in recently-established ARs/MPAs initiatives and more extensively throughout Hong Kong and adjacent PRC inshore waters.
TABLE OF CONTENTS
| Directors Foreword T.J. Pitcher | 3 |
| 1. Introduction, Background and Study Objectives (T. J. Pitcher, E.A. Buchary, U.R. Sumaila and N. Haggan) | 4 |
| 2. New ECOPATH Models of the Hong Kong Marine Ecosystem (E.A. Buchary, T.J. Pitcher, W.L. Cheung and T. Hutton) | 6 |
| 2.1 Defining and parameterizing the model | 6 |
| 2.2 Landing and discard database applied | 7 |
| 2.3 Results | 9 |
| 2.4 Revised ECOPATH model the system after 5 years closure | 14 |
| 3. Revision of the Hong Kong Catch Estimates (T.J. Pitcher) | 17 |
| 3.1 Methods applied in revising the catch estimates | 17 |
| 3.2 Results | 18 |
| 4. Temporal Simulation using ECOSIM (E.A. Buchary and T.J. Pitcher) | 19 |
| 4.1 Setting up ECOSIM simulation routine | 19 |
| 4.2 Feeding behavior parameters | 19 |
| 4.3 Trophic ontogeny | 21 |
| 4.4 Flow control assumption | 21 |
| 4.5 Mediation factor | 22 |
| 4.6 Fishing effort trajectory and assumptions | 24 |
| 4.7 Biomasses depleted under baseline assumptions | 25 |
| 5. ECOSPACE simulations for Hong Kong waters (T.J. Pitcher and E.A. Buchary) | 27 |
| 5.1 Management area designation | 27 |
| 5.2 Habitat designation and assignation of functional groups into different habitats | 29 |
| 5.3 Dispersal rate, predation and foraging parameters | 31 |
| 5.4 Assignation of fisheries sectors into different habitats and management areas | 32 |
| 6. ECOSPACE simulations for the People's Republic of China (PRC) inshore waters (T.J. Pitcher and E.A. Buchary) | 36 |
| 6.1 Underlying assumptions | 36 |
| 6.2 Management area designation and mapping | 37 |
| 6.3 Habitat and management area designation and assignation of functional groups into different habitats | 38 |
| 6.4 Assignation of fisheries sectors into different habitats and management areas | 40 |
| 7. Assumptions of ECOPATH, ECOSIM and ECOSPACE in this study (E.A. Buchary and T.J. Pitcher) | 45 |
| Part 2. Hong Kong MPAs and ARs | |
| 8. Management scenarios tested and analyzed (E.A. Buchary and T.J. Pitcher) | 46 |
| 8.1 Ecosystem model of Hong Kong waters | 46 |
| 8.2 Ecosystem model of PRC inshore waters: an extension of HK model | 49 |
| 9. Economic analysis and simulations of Hong Kong fisheries (U.R. Sumaila) | 50 |
| 9.1 Introduction | 50 |
| 9.2 General outline of the approach used for the analysis | 50 |
| 9.3 Valuation of changes in quantity harvested | 51 |
| 9.4 Determining artificial reef deployment and fish harvesting costs | 51 |
| 9.5 Weighting present and future streams of income | 51 |
| 9.6 The analysis | 51 |
| 9.6.1 Project benefits | 51 |
| 9.6.2 Project costs | 51 |
| 9.6.3 Analysis and comparison of annual benefits | 52 |
| 9.6.4 Game theoretic analysis | 52 |
| 10. Discussion and concluding remarks (T.J. Pitcher, U.R. Sumaila, E.A. Buchary and N. Haggan) | 54 |
| 10.1 Main ecological results and discussion | 54 |
| 10.1.1 Comparison of reef resources across scenarios | 54 |
| 10.1.2 Comparison of indicator species across scenarios | 55 |
| 10.2 Main economic results and discussion | 57 |
| 10.2.1 Potential benefits from the different scenarios analyzed | 57 |
| 10.2.2 Reef fish benefits | 57 |
| 10.2.3 Benefits from key commercial resources | 59 |
| 10.2.4 Comparison of ecological and economic outcomes | 59 |
| 10.2.5 Cooperative and non-cooperative outcomes | 60 |
| 10.3 Resumption of fishing after closure in Hong Kong and PRC inshore waters | 62 |
| 10.4 Management policy implications of the current ARs/FPA plans | 64 |
| 10.5 Conclusions and Recommendations | 69 |
| References | 70 |
ANNEXES
| 1. Construction of the ECOPATH Model of Hong Kong Waters in the 90s a. Composition of functional groups in the revised ECOPATH model b. Model inputs as extracted from the Ecowrite routine of ECOPATH | 73 |
| 2. Results - the Ecological and Economic Simulations of the HK Model | 97 |
| 3. Results from the Ecological Simulations of the PRC Model a. Maps of habitats and management areas b. Maps of biomass by resources and fishing effort from simulations c. Tables of simulated catch and biomass by resource and fishery sector | 145 |
| 4. Economic Data and Results Pages a. Computed prices by functional groups b. Harvesting cost data by vessel type supplied by AFCD c. Enforcement and deployment cost computed from data supplied by AFCD d. Annual benefits from key commercial resources per km2 | 163 |

