Biogeochemical cycling and phyto- and bacterioplankton ... ?· dissolved organic carbon and nitrogen…
Post on 03-Dec-2018
Embed Size (px)
Biogeosciences, 14, 959975, 2017www.biogeosciences.net/14/959/2017/doi:10.5194/bg-14-959-2017 Author(s) 2017. CC Attribution 3.0 License.
Biogeochemical cycling and phyto- and bacterioplanktoncommunities in a large and shallow tropical lagoon (TrminosLagoon, Mexico) under 20092010 El Nio Modokidrought conditionsPascal Conan1, Mireille Pujo-Pay1, Marina Agab1, Laura Calva-Bentez2, Sandrine Chifflet3, Pascal Douillet3,Claire Dussud1, Renaud Fichez3, Christian Grenz3, Francisco Gutierrez Mendieta2, Montserrat Origel-Moreno2,3,Arturo Rodrguez-Blanco1, Caroline Sauret1, Tatiana Severin1, Marc Tedetti3, Roco Torres Alvarado2, andJean-Franois Ghiglione11Sorbonne Universits, UPMC Univ Paris 06, CNRS, Laboratoire dOcanographie Microbienne (LOMIC),Observatoire Ocanologique, 66650, Banyuls/mer, France2Universidad Autnoma Metropolitana, Departamento de Hidrobiologa, Mxico D.F., Mexico3Aix-Marseille Universit, CNRSINSU, Universit de Toulon, IRD, Mediterranean Institute of Oceanography (MIO)UM 110, 13288, Marseille, France
Correspondence to: Pascal Conan (email@example.com)
Received: 8 July 2016 Discussion started: 11 August 2016Revised: 6 January 2017 Accepted: 25 January 2017 Published: 2 March 2017
Abstract. The 20092010 period was marked by an episodeof intense drought known as the El Nio Modoki event. Sam-pling of the Trminos Lagoon (Mexico) was carried out inNovember 2009 in order to understand the influence of theseparticular environmental conditions on organic matter fluxeswithin the lagoons pelagic ecosystem and, more specifi-cally, on the relationship between phyto- and bacterioplank-ton communities. The measurements presented here concernbiogeochemical parameters (nutrients, dissolved and partic-ulate organic matter [POM], and dissolved polycyclic aro-matic hydrocarbons [PAHs]), phytoplankton (biomass andphotosynthesis), and bacteria (diversity and abundance, in-cluding PAH degradation bacteria and ectoenzymatic activ-ities). During the studied period, the water column of theTrminos Lagoon functioned globally as a sink and, moreprecisely, as a nitrogen assimilator. This was due to thehigh production of particulate and dissolved organic matter(DOM), even though exportation of autochthonous matter tothe Gulf of Mexico was weak. We found that bottom-upcontrol accounted for a large portion of the variability of phy-toplankton productivity. Nitrogen and phosphorus stoichiom-etry mostly accounted for the heterogeneity in phytoplank-ton and free-living prokaryote distribution in the lagoon. In
the eastern part, we found a clear decoupling between ar-eas enriched in dissolved inorganic nitrogen near the PuertoReal coastal inlet and areas enriched in phosphate (PO4) nearthe Candelaria estuary. Such a decoupling limited the poten-tial for primary production, resulting in an accumulation ofdissolved organic carbon and nitrogen (DOC and DON, re-spectively) near the river mouths. In the western part of thelagoon, maximal phytoplankton development resulted frombacterial activity transforming particulate organic phospho-rus (PP) and dissolved organic phosphorus (DOP) to avail-able PO4 and the coupling between Palizada River inputs ofnitrate (NO3) and PP. The Chumpan River contributed onlymarginally to PO4 inputs due to its very low contribution tooverall river inputs. The highest dissolved total PAH concen-trations were measured in the El Carmen Inlet, suggestingthat the anthropogenic pollution of the zone is probably re-lated to the oil-platform exploitation activities in the shallowwaters of the southern of the Gulf of Mexico. We also foundthat a complex array of biogeochemical and phytoplanktonicparameters were the driving force behind the geographicaldistribution of bacterial community structure and activities.Finally, we showed that nutrients brought by the PalizadaRiver supported an abundant bacterial community of PAH
Published by Copernicus Publications on behalf of the European Geosciences Union.
960 P. Conan et al.: Trminos Lagoon, Mexico
degraders, which are of significance in this important oil-production zone.
Coastal lagoons are complex environments, combining fea-tures of shallow inland waterbodies wholly or partly sealedoff from the adjacent coastal oceans. They are influencedby tides, river inputs, the precipitation versus evaporationbalance, and the surface heat balance. Interactions betweenfreshwater and marine sources generate strong gradientsof salinity, light, and nutrient availability (Hauenstein andRamrez, 1986). Biological diversity is generally high inthese environments (Milessi et al., 2010). Located in thesouthern Gulf of Mexico near Campeche Sound, the Tr-minos Lagoon is one of the largest tropical coastal lagoonsworldwide, and its recognized environmental importance andprotected status are potentially threatened by petroleum-related industrial activities inshore and offshore (Garca-Roset al., 2013). A first tentative budget of salt and nutrients con-cluded that the Trminos Lagoon was slightly autotrophicon a yearly basis (David, 1999), but this assessment wasclearly based on scarce environmental data. Chlorophyll a(Chl a) concentration and phytoplankton net production havebeen reported to range from 1 to 17 g L1 and from 20 to300 gC m2 yr1 respectively (Day et al., 1982), suggestinga potential shift from oligotrophic to eutrophic conditions.
In aquatic ecosystems, bacteria utilize a large fraction (upto 90 %) of the primary production, since algal carbon ex-udates can be the principal source for bacterial production(Cole et al., 1988; Conan et al., 1999). Besides the utiliza-tion of a considerable part of the available organic matter,bacterioplankton communities also absorb inorganic nutri-ents, thus competing with phytoplankton communities (Co-nan et al., 2007; Hobbie, 1988). The bulk of the organic mat-ter is a highly heterogeneous matrix which is primarily com-posed of complex and refractory substrates (Hoppe et al.,2002), but which also contains labile substrates such as pro-teins or peptides, oligosaccharides, and fatty acids. Extracel-lular enzymes are thus essential to aquatic microorganisms asthey allow for the partitioning of complex organic substrates,including high molecular weight compounds which cannotpass through the cell membrane (Arnosti and Steen, 2013).As a function of genetic diversity, the capacity to produce ex-tracellular enzymes is differently distributed in the bacterialcommunity, directly impacting the range of substrates me-tabolized (Zimmerman et al., 2013). This phenomenon hasglobal-scale implications since several meta-analyses haveclearly evidenced differences in the metabolic capacities ofmicroorganisms from temperate, tropical, or high latitudewaters (Amado et al., 2013; Arnosti et al., 2011). At a lo-cal scale, alteration of the evaporationprecipitation balancedue to climate change can be challenging, especially in the
case of a coastal lagoon, as it is well known that changesin salinity may alter bacterial diversity and activity (Pedrs-Ali et al., 2000). Local anthropogenic inputs of organicpollutants such as polycyclic aromatic hydrocarbons (PAHs)may also affect bacterial diversity and activity (Aguayo et al.,2014; Jimnez et al., 2011; Rodrguez-Blanco et al., 2010).Indeed, PAHs, which can comprise as much as 2535 % oftotal hydrocarbon content in crude oils (Head et al., 2006),are among the most abundant and ubiquitous pollutants inthe coastal environment (Gonzlez-Gaya et al., 2016). Thesecompounds are recognized by the European and US environ-mental agencies as priority pollutants for the aquatic mediumdue to their toxicity, persistence, and ability to accumulate inthe biota (Kennish, 1992). Hence, the presence of PAHs inthe marine environment may induce an increase in the in-digenous populations of marine bacteria that can break downand utilize these chemicals as a carbon source, the so-calledPAH-degrading bacteria or PAH degraders. These bac-teria are generally strongly selected in oil-impacted ecosys-tems, where they may account for 70 to 90 % of the total bac-terial community (Gutierrez et al., 2014; Head et al., 2006).
Despite their importance, few studies have consideredthe bacterial communities of tropical inland aquatic ecosys-tems (Roland et al., 2010) or coastal lagoons (Abreu et al.,1992; Hsieh et al., 2012; MacCord et al., 2013; They et al.,2013) and almost none have dealt with tropical coastal la-goons (Scofield et al., 2015). Among the existing studies,very few have been conducted on bacterial communities andmost of them have been based on culture-dependent meth-ods (Lizrraga-Partida et al., 1987, 1986). However, cul-tivable bacteria represent a very small fraction of the totalpresent bacteria (< 0.1 %; Ferguson et al., 1984), and culture-independent methods are needed to more accurately assessthe diversity and activity of whole bacterial communities insuch a vast and understudied system. Additionally, the Tr-minos Lagoon is potentially impacted by PAHs which maycome from a variety of sources which all carry various ur-ban and industrial wastes (fuel combustion and traffic ex-haust emissions) including sea-based activities (ballast wa-ter discharge, drilling, and spills from ships, platforms andpipelines), rivers, surface runoffs, and the atmosphere. Nev-ertheless, to our knowledge, little is known about the PAHcontent in this ecosystem. Even though Norea-Barroso etal. (1999) reported on PAH concentrations in the Ameri-can oyster Crassostrea virginica and Osten-Von Rendon etal. (2007) studied PAH concentrations in surface sediments,no data are currently available concerning dissolved PAHconcentrations in the surface waters of the Trminos Lagoon.
Our study aims to evaluate the link between (i) biogeo-chemical (nutrients, dissolved and particulate organic matter[POM]), (ii) phytoplanktonic (biomass and photosyntheticact