one of its natural characteristics. On evolutionary time-scales this instability within <strong>and</strong> between years is favorableto small plankton-eating fish with high fecundity <strong>and</strong> rapid generation times that can exploit unpredictable periodsof exceptional high productivity <strong>and</strong> persist through periods of exceptionally low productivity.The high biomass of these, mostly schooling, water-column dwelling species, collectively termed “small pelagics,”are the foundation <strong>and</strong> mainstay of the fishery of Ghana. Their life cycles, adapted to exploit times of highproductivity, can be resilient to even high fishing pressure <strong>and</strong> can sometimes recover rapidly fromoverexploitation (Bakun, 1998). Additionally, the small pelagics, because of their richness in oils <strong>and</strong>micronutrients, provide quality nutrition (e.g., Lokko et al., 2004). Small pelagic species dominate the catch, butin the sea, they are preyed upon by a high diversity of high-value, large pelagic species in Ghana’s fishery (e.g.,tunas, billfish, <strong>and</strong> marlin). The productivity supported by the upwelling system also increases productivity on thesea floor, supporting a rich fauna of demersal, or bottom-dwelling, fish on the continental shelf of Ghana. About90 lagoons along Ghana’s coast are also among the available habitats for marine resources, <strong>and</strong> provide vitalseasonal income <strong>and</strong> subsistence fish <strong>and</strong> crustacean catches for nearby communities (Finegold et al., 2010).The productive marine ecosystem of Ghana has supported a massive increase in fishing yield since the 1970s, butstrong signals indicate it is under increasing strain (Koranteng <strong>and</strong> Pauly, 2004; Finegold et al., 2010). Catch ofprominent species in the fishery have declined; most notably those high in the food web as is often the case inheavily exploited systems (Pauly et al., 1998; Koranteng <strong>and</strong> Pauly, 2004), but also more recently the small preyspecies (Bannerman <strong>and</strong> Cowx, 2002; Koranteng, 2004; Finegold et al., 2010). Striking, sudden system shifts(disappearance <strong>and</strong> appearance of fish species, e.g., round sardinella Sardinella aurita; sudden proliferation ofotherwise uncommon species) can at least in part be attributed to high fishing pressure (Koranteng <strong>and</strong> Pauly,2004). These observed <strong>change</strong>s indicate the future of the services provided by marine <strong>and</strong> coastal habitats are byno means assured (Finegold et al., 2010). The vulnerabilities of this system are multi-faceted with or withoutconsideration of <strong>climate</strong> <strong>change</strong>.MARINE FISHING FLEETOne of the most notable <strong>change</strong>s in recent decades is the tremendous growth in fleet size in nearly every category(Table 18), one, but only one indication of the increasing pressure being put on the marine fishery resource. Thefleet today can be divided into 5 primary categories; the canoe fleet, the inshore fleet, the industrial fleet, the tunafleet, <strong>and</strong> an extremely data poor segment, the coastal lagoon fisheries (Table 18, Ferraris <strong>and</strong> Korangeng, 2004;Dontwi et al., 2008; Finegold et al., 2010). A host of other biological symptoms of decline coupled with <strong>change</strong>sin fishing practices also emphasizes the increasing <strong>vulnerability</strong> of the marine fishery resource without anyconsideration of <strong>climate</strong> <strong>change</strong> (Table 19; see also State of the marine fishery).Canoe Fleet: The canoe fishery is the most numerous <strong>and</strong> diverse fleet segment in Ghana, harvesting fishes fromall resource sectors: large pelagic fish (tuna, billfish, sharks) by drift gillnets <strong>and</strong> hook <strong>and</strong> line gear; small pelagicfish via purse <strong>and</strong> beach seines; <strong>and</strong> demersal species with set nets <strong>and</strong> beach seines. Ghanaian canoe fishers areadaptable using >20 identifiable gear types (Doyi <strong>and</strong> Neequaye, 1990; Marquette et al., 2002) in the fishery toincrease catch efficiency. The canoe fleet can be further subdivided by size, which also reflects the types of gearemployed (Finegold et al., 2010).Small or “one man canoes,” typically 4-5m long <strong>and</strong> powered by paddle or sail, are used inshore for line fishing,small gill nets, <strong>and</strong> cast nets (especially in lagoons). During the last canoe census (2004), small canoes comprisedonly 5 percent of the surveyed canoe fleet. Subsistence fishing, particularly in lagoons, is not captured in l<strong>and</strong>ingstatistics (Finegold et al., 2010).Mid-sized canoes are 6-11 m long, typically crewed by 2-11 fishers, propelled by sail, paddle, or 8-40 hp motors(depending on length), <strong>and</strong> are used primarily for bottom-set, floating, or drifting gill nets <strong>and</strong> line fishing. Someare also used with smaller beach seine nets (Finegold et al., 2010).Large canoes are 11-17 m long, crewed by 10-25 fishers, <strong>and</strong> propelled primarily by 40 hp motors. The largecanoe category can be subdivided into the larger Ali/Poli/Watsa (APW) canoes <strong>and</strong> the large beach-seine canoes(Finegold et al., 2010). The former are named after the type of traditional fishing gear once used: “ali” nets were106 GHANA CLIMATE CHANGE VULNERABILITY AND ADAPTATION ASSESSMENT
gill nets constructed from traditional fibres; poli <strong>and</strong> watsa nets are types of purse seine. Gear types have evolvedconsiderably over the last century. Large canoes also employ large drift nets (e.g., the “nifa-nifa” net). Largebeach-seine canoes make up the second sub-category; these usually have high planking at the bow to prevent largewaves coming on board when operating in the surf (Finegold et al., 2010).Without registration requirements <strong>and</strong> no limits on access to the fishery, the number of active canoes in Ghanahas continually increased from 7,000 in 1980 to an estimated current fleet size of 13,500 (projected from lastcanoe survey in 2004, Finegold et al., 2010). From 1970 to 1980, about 85 percent of all canoes were reported tobe motorized; now the figure has fallen to a fairly consistent 55 percent. Substantial growth occurred in motorizedcanoes, canoes, <strong>and</strong> canoe fishers in all coastal administrative regions from 1995-2004, but growth was notablystrong in the Western Region which now represents about 36 percent of the canoe fleet of Ghana (Finegold et al.,2011).Semi-industrial or inshore fleet: The semi-industrial or inshore fleet consists of mostly locally-built, plankedwooden-hulled vessels (8-30 m long) with inboard diesel engines (90-400 hp) (Bannerman <strong>and</strong> Cowx, 2002; DoF,2003; Nunoo et al., 2009). These vessels use trawling gear to catch demersal fish <strong>and</strong> purse seines to capture smallpelagic fish during the major <strong>and</strong> minor upwelling periods. Smaller vessels in this class are generallyunderpowered for trawling <strong>and</strong> with the adoption of light fishing in the minor or low seasons, they have tended tospecialize in purse seining. Most purse seine nets are 400-800 m long <strong>and</strong> 40-70 m deep with a mesh size of 25-40mm; nets >2 km long are used by the large vessels. First deployed in Ghana in 1948, the numbers of these vesselsquickly peaked in the early 1970s. Following steep decline from the early 1990s to early 2000s, vessel numbersrose sharply again through early 2000s, an impending warning sign of significantly increasing effort <strong>and</strong> perhapsstock overexploitation. The rapid <strong>and</strong> continued increase in this fleet likely relates to the adoption of light fishing,<strong>and</strong> the associated year-round access to the small pelagic resource (Finegold et al., 2010).Industrial fleet: The industrial fleet consists of large, steel hulled foreign-built vessels that are further distinguishedfrom the inshore fleet by their ability to freeze fish at sea, <strong>and</strong> hence, their ability to stay at sea for long periods oftime (Finegold et al., 2010). Apart from the tuna fleet (see subsequent), the industrial fleet largely engages indemersal trawling. A sub-fleet targeting shrimp operated in the 1990s (22 operational vessels maximum); however,since 2002 only two operational shrimpers were reported. Another sub-fleet consists of ships practicing pairtrawling, in which two industrial vessels pull a trawl net between them. Pair trawling was introduced in 2000, <strong>and</strong>the fleet grew to 20 vessels before the practice was banned in 2008. Though pair trawlers were supposed to be refittedas single trawlers following the ban, some may still be operating in pairs, leaving port separately <strong>and</strong> meetingup at sea. Fishermen in the Western Region continue to report observing pair trawlers operating off the coast(Finegold et al., 2011).The industrial fleet has steadily exp<strong>and</strong>ed with a sharp increase over the last three decades when governmentpolicy targeted this fleet to promote fishery development <strong>and</strong> improved incomes from the sector. A problematicgap in the Ghanaian sampling system is that industrial vessels provide information on their own catches (selfreport), <strong>and</strong> no method is in place to verify the information provided. Extremely low catch <strong>and</strong> effort arereported by this fleet, so low it is inconceivable they could make a profit, providing strong indications that vesselssubstantially under-report catches (Finegold et al., 2010). Given the catch potential of these large vessels <strong>and</strong> theirability to stay at sea for long periods <strong>and</strong> transship catch to places other than Ghana, better data on this fleetsegment is urgently required. The industrial fleet also supports another emergent but illegal “fishery”; one whereso called “trash fish” (low value, small or damaged fish) are transferred at sea from trawlers to canoes speciallymodified to transport large volumes of fish (Nunoo et al., 2009). These fish then enter the normal beach-basedmarket chain as accessed by canoe fishers. If this trade continues, Ghana’s long-st<strong>and</strong>ing traditional fishingvocation, which is ranked among the best in West Africa (Atta-Mills et al., 2004) may be lost. Also, the increase indiscards on the market tends to encourage offshore vessels to fish much closer to shore <strong>and</strong> also to use small,illegal mesh sizes. The continuation of trash fish trade puts more pressure on Ghana’s depleting fish stocks, yetanother situation that may push the already overfished stocks towards collapse. In addition, a government subsidyon fuel for artisanal fisheries, which is supposed to be used for legal fishing activities, is channeled into transshipmentof catch at sea (Nunoo et al., 2009).GHANA CLIMATE CHANGE VULNERABILITY AND ADAPTATION ASSESSMENT 107
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GHANA CLIMATE CHANGEVULNERABILITY A
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GHANACLIMATE CHANGEVULNERABILITY AN
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ACRONYMSCAADPCBOCCCDCSCEACEPFCFMCIC
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NGONCRCNREGNRMNTFPPAPAMSCPPGRCRAMSA
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EXECUTIVE SUMMARYCountries in Afric
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precipitation changes is not very d
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AGRICULTURE AND LIVELIHOODSAgricult
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would include concentrating access
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of transparency pervade the current
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alternate energy sources (i.e., fos
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affecting carbon sequestration. Adv
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Information and analysis needs for
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1. INTRODUCTIONThe West African cou
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ABFigure 2.1 Two approaches to vuln
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Mean Annual Temperature (C)2928.528
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The UNDP-NSCP country-level climate
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For most eco-climatic zones, five-y
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increases generally were projected
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Table 3.2 Potential change in tempe
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parameter (temperature and precipit
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emission scenarios gives a decrease
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of finance and economic planning, f
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indigenous people and more recently
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Phase 1 REDD ReadinessConsultations
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SC. A New National Plantation Devel
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to be developed that provide rigoro
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LandownerTable 4.1 Land Ownership i
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ProblemTable 4.2 Problems Associate
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TENURE CONSIDERATIONS IN LIGHT OF C
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the south of the Ashanti Uplands re
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(interview). An opportunity exists
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Upper West Region, 69.8 percent of
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Brong-Ahafo Region that entails ref
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Ghana Limited, 2009). Given the con
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positive impacts, and has upset com
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Basin (total area 416,382km 2 ) lie
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effect. In the drier scenario, the
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Communities are, rightly or wrongly
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carbon sequestration and maintenanc
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Information and analysis needs for
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Table 11.1 Options for intervention
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Barriers toAdaptation andMitigation
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Barriers toAdaptation andMitigation
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Barriers toAdaptation andMitigation
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Amanor, K.S. 2001. Share contracts
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Braimoh, A. and P. Vlek (2006). "So
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Energy Commission. 2005. Strategic
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Gyau-Boakye P., and Tumbulto J.W. 2
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Koranteng, K.A. 1995. The Ghanaian
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MSE (Ministry of Science and Agricu
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Rubin, J.A.; Gordon, C.; Amatekpor,
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Wagner, M.R. and Cobbinah, J.R., 19
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Date Organization Interviewee Posit
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Date Organization Interviewee Posit
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Date Organization Interviewee Posit
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APPENDIX 2. TEAM MEMBERSName Role B
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DP - contact person Activity Object
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APPENDIX 5. SCENARIOS OF TEMPERATUR
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e. RAIN FOREST ZONEBaseline Mean Te
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Aug 191.5 16 12.0 -0.1 -0.5 -1.0 19
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Feb 25.6 3 9.4 -9.1 -29.7 -58.9 23.
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c. TRANSITIONAL ZONEBaseline Mean T
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APPENDIX 8. SCENARIOS OF CHANGES IN
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d. DECIDUOUS FOREST ZONEBaseline Me
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APPENDIX 9. SCENARIOS OF MEAN SEA S
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U.S. Agency for International Devel