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Evidence of Localised Upwelling in Pemba Channel (Tanzania) During the Southeast Monsoon

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Evidence of Localised Upwelling in Pemba Channel (Tanzania) During the Southeast Monsoon Ocean and Coastal Management 200 (2021) 105462 Contents lists available at ScienceDirect Ocean and Coastal Management journal homepage: http://www.elsevier.com/locate/ocecoaman Evidence of localised upwelling in Pemba Channel (Tanzania) during the southeast monsoon Stuart C. Painter a,*, Baraka Sekadende b, Angelina Michael c,e, Margaux Noyon d, Salome Shayo b, Brian Godfrey d, Mtumwa Mwadini c, Margareth Kyewalyanga c a National Oceanography Centre, Southampton, UK b Tanzania Fisheries Research Institute, Dar es Salaam, Tanzania c Institute of Marine Sciences, University of Dar es Salaam, Tanzania d SA-UK Bilateral Chair: Ocean Science & Marine Food Security, Nelson Mandela University, Port Elizabeth, South Africa e College of Natural and Mathematical Sciences, University of Dodoma, Tanzania ARTICLE INFO ABSTRACT Keywords: Oceanographic and biogeochemical observations collected in Pemba Channel, a deep-water (800 m) channel East african coastal current separating Pemba Island from mainland Tanzania, during the South East monsoon indicate the presence of active Pemba channel upwelling along the western edge of Pemba Island. Surface salinity values, nutrient concentrations and the Upwelling presence of coccolithophore species previously reported from the mid to lower euphotic zone all suggest up­ Western indian ocean 3 welling from at least 80–100 m depth. The surface waters of the channel were characterised with low NO3 :PO4 Biogeochemistry (0.68:1) and NO3 :Si (0.04:1) ratios far below the Brzezinski-Redfieldratio indicating the presence of N-limitation Phytoplankton Coccolithophores and the possibility that these waters may be susceptible to anthropogenic N inputs. Surface NO3 concentrations 1 1 Gephyrocapsa averaged 0.09 ± 0.10 μmol L but increased to 0.5 μmol L in the centre of upwelling where coincidentally both integrated nutrient concentrations and surface POC/PON pools were approximately 2-fold higher than the channel average. Despite its significance for local productivity upwelling is tentatively estimated, via stoichio­ metric assumptions, to enhance local productivity by only 20%. The modest productivity response to upwelling may be explained by picoplankton (0.2–2 μm) dominance of the phytoplankton community with this size-class representing ~80% of total chlorophyll-a. Nevertheless, important spatial variability was identifiedin larger size fractions and supported by taxonomic analyses with indications that the distribution of Chaetoceros spp. alone may be particularly relevant for understanding the variability in larger (>20 μm) chlorophyll-a size fractions. The location of upwelling has previously been shown to host large concentrations of small pelagic fish thus management of this regionally important resource would benefitfrom additional investigation of the underlying physical mechanism driving upwelling and subsequently how trophic interactions and ecosystem productivity are influenced. 1. Introduction likely to impede effective management decision making (Van der Elst and Everett 2015). Sustainable management of the natural ocean resources of the This is particularly true for that section of the East African coastline Western Indian Ocean is increasingly recognised as being central to the influenced by the East African Coastal Current (EACC), where extant socio-economic future of the region (Obura et al., 2017). It is estimated oceanographic observations are limited, biogeochemical measurements that around 60 million people, approximately one-third of the regional are sparse, and many key results are now several decades old, difficultto population, live within 100 km of a coastline with many dependent upon access, contradictory, or of questionable quality (Painter 2020). Such a the ocean for employment and for their primary source of protein (van situation hampers efforts to effectively and sustainably manage marine der Elst et al., 2005; Taylor et al., 2019). There is however, growing resources, complicates efforts to produce regional environmental syn­ awareness that historic under sampling of the Western Indian Ocean is theses and leaves many basic questions about the marine environment * Corresponding author. E-mail address: [email protected] (S.C. Painter). https://doi.org/10.1016/j.ocecoaman.2020.105462 Received 13 May 2020; Received in revised form 28 October 2020; Accepted 22 November 2020 Available online 7 December 2020 0964-5691/© 2020 The Author(s). Published by Elsevier Ltd. This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/). S.C. Painter et al. Ocean and Coastal Management 200 (2021) 105462 and how it may respond in future unanswerable. identified contrasting nutrient enrichment mechanisms at work during ◦ The region influenced by the EACC (~3–11 S) formally lies within different monsoon seasons. Whilst traditional wind-driven upwelling the Exclusive Economic Zones of Tanzania and Kenya. Swallow et al. was found to explain enhanced phytoplankton biomass along the coast (1991), determined that the core of the EACC lies seaward of the narrow during the northeast monsoon, the larger biological response during the continental shelf but that the current’s influence is negligible beyond southeast monsoon results from the dynamic uplift of isopycnal and 200 km offshore. Along the coastline of Tanzania complex bathymetry nutrient isopleths as the EACC approaches the coast coupled with hor­ allows the EACC to approach close to the mainland. The Pemba Channel izontal advection of nutrients by stronger southeasterly winds. ◦ ◦ (~5.2 S, 39.3 E), separates the island of Pemba from the East African Environmental conditions within Pemba Channel and along the mainland and is one of three narrow seaways found along the Tanzanian Tanzanian coast are of interest due to the socioeconomic and food se­ ◦ coast. Together with the neighbouring Zanzibar Channel (~6 S) near curity significance resident small pelagic fish populations play (Ander­ ◦ Unguja (Zanzibar) Island and Mafia Channel (~8 S) near Mafia Island, son and Samoilys 2016; Taylor et al., 2019; Sekadende et al., 2020). The these seaways provide important foci for artisanal and subsistence channel and the wider EACC influenced region are also unique for a fishingcommunities due to the sheltered waters they offer and the ease tropical coastal ecosystem as significant monsoon driven seasonality of access for traditional fishing vessels. Pemba Channel is unique impacts the upper ocean making the region unlike comparable tropical amongst these three seaways in that it is the only deep water channel coastal ecosystems of the Atlantic and Pacific Oceans (Newell 1957, (~800 m deep, ~40 km wide) found along the Tanzanian coast and is 1959; Leetmaa 1972; Wyrtki 1973; Harvey 1977; Bryceson, 1982; thus suggested to have an important role in bringing nutrient rich in­ McClanahan 1988). Consequently, adoption of management practices termediate depth oceanic waters from the open Western Indian Ocean from elsewhere may not be appropriate and improved knowledge of the close to the coast, most likely facilitated by the limb of the EACC that environmental conditions in Pemba Channel is thus central to improved passes through the Pemba Channel (Semba et al., 2019). Upwelling of environmental and fisheries management. Here oceanographic and nutrient rich water along the Tanzanian coast has long been suggested biogeochemical observations from Pemba Channel made during the SE (Bakun et al., 1998), and could be significantfor primary production and monsoon period are presented to complement ongoing efforts to un­ hence for local fisheries,but until recently direct evidence for upwelling derstand and manage these waters more effectively. was equivocal or wrongly attributed. Jebri et al. (2020) have now Fig. 1. Map showing the study location in the Western Indian Ocean (inset image) and sampling stations within Pemba Channel. 2 S.C. Painter et al. Ocean and Coastal Management 200 (2021) 105462 2. Methods was determined as the depth where the total nitrate concentration reached 1 μmol L 1 using interpolated vertical profiles (due to the low 2.1. Oceanographic survey vertical sampling resolution). A 10-day research cruise through the Pemba Channel was conducted 2.5. Particulate organic carbon and nitrogen between June 30th and July 9th, 2019 using the M.Y. Angra Pequena, a 24 m expedition yacht fitted with a Palfinger crane on the foredeck Particulate organic carbon (POC) and nitrogen (PON) concentrations allowing deployment of a small CTD system to ~500 m. Maximum and the associated isotopic content were determined via coupled sampling depths ranged from 50 m to 500 m depending upon local ba­ elemental analysis and mass spectrometry. One litre seawater samples ◦ thymetry and maximum wire out (500 m). In the deep waters of the were filtered under vacuum onto ashed (450 C, >4 h) GFF filters and central channel sampling to 500 m was often challenging due to the rinsed with a pH buffered solution (~pH 8) of pure water (1 L pure water strength of the northward flowingEACC and maximum sampling depths plus 800 μl of ammonium solution) before filters were placed in 2 mL ◦ were variable. Forty stations were sampled with an approximate hori­ cryo-vials and dried overnight at 40 C. In the laboratory, filters were zontal spacing of ~11 km over the slopes and deeper parts of the channel extracted and fumed with concentrated HCl to remove inorganic carbon ◦ (Fig. 1). Vertical profiles of temperature, salinity, chlorophyll-a
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