Impacts of hydroclimatic variability on surface water and porewater dissolved organic matter in a semi-arid estuary
Introduction
Estuarine dissolved organic matter (DOM) consists of a diverse array of allochthonous (i.e., terrestrial runoff, river discharge, and benthic fluxes) and autochthonous (i.e., phytoplankton metabolism and excretion, viral lysis, and sloppy feeding) sources (Carlson and Hansell, 2015; Repeta, 2015; Sipler and Bronk, 2015). Annually, an estimated 0.25 × 1015 g C are transported from land to the sea in the form of dissolved organic carbon (DOC) (Hedges et al., 1997) while the DOM sediment benthic fluxes are equivalent to riverine fluxes in coastal regions (Burdige et al., 1999). However, these estimated fluxes may underestimate allochthonous DOC fluxes to regions where groundwater discharge, diffuse sediment fluxes, and effects of extreme wet events (e.g., flooding and drought) are still not well constrained (Webb et al., 2019).
Generally, bulk DOC concentrations decrease along salinity gradients from the river to the open ocean while the DOM composition is simultaneously changing. With increasing salinity, it is expected the molecular weight, carbohydrate content (Abdulla et al., 2010a), heteroelement content (Sleighter and Hatcher, 2008), photoammonification (Aarnos et al., 2012), and lability (D'Andrilli et al., 2015) will increase while the aromaticity (Abdulla et al., 2010a), photoproduction of dissolved inorganic carbon (DIC) (Aarnos et al., 2012), and carbon:nitrogen (C:N) ratio (Sipler and Bronk, 2015) of the DOM decreases. In tropical and temperate marine basins, the riverine DOM pool is rapidly transformed through a multitude of biotic (microbial) and abiotic (photochemical) processes (Spencer et al., 2009), such that terrigenous DOC constitutes approximately 1–2% of total DOC in the oceans (Hernes and Benner, 2006). Thus, the molecular composition of terrestrially derived DOM appears to have reduced concentrations and less richness than marine DOM (Abdulla et al., 2010b; Medeiros et al., 2015; Powers et al., 2018).
The quantity and composition of riverine DOM was shown to affect biogeochemical cycling in estuaries with magnitudes that vary with changes in hydroclimatic conditions (Letourneau and Medeiros, 2019; Liu and Lu, 2019; Majidzadeh et al., 2017; Raymond and Saiers, 2010; Spencer et al., 2009). Additionally, changes in riverine DOM composition have been shown to lag behind changes in DOM fluxes during storm events (Yang et al., 2013). Extreme flooding events result in large “pulse” releases of terrestrial DOM (tDOM) into fluvial systems, thus, increasing DOM concentrations that are “shunted” rapidly downstream due to increased discharge and flushing (Raymond et al., 2016). A survey of 31 forested watersheds in the eastern United States, demonstrated that 86% of annual DOC export occurs following major precipitation events and that 60% of this export occurs during large flow events that account for 5% of the year (Raymond and Saiers, 2010). For example, during a storm event three small watersheds in Oregon were shown to experience approximately 3-fold increases in DOC concentrations with an increase in the proportion of humic DOM (Hood et al., 2006). Thus, low-frequency large flow events, anticipated to increase with climate change (Stocker, 2014), are responsible for a significant portion of annual tDOM input to estuaries and coastal oceans. Furthermore, the export of DOM during extreme wet events approaches the mean annual DOM export during non-extreme flow event years (Asmala et al., 2021; Caverly et al., 2013; Jung et al., 2014; Raymond and Saiers, 2010; Sánchez-Murillo et al., 2019; Yoon and Raymond, 2012). Therefore, in the face of a rapidly changing climate, there is an immediate need to understand the mechanisms that control the fate and transport pathways of DOM for successful management of aquatic food webs and sustainable ecosystem health.
To date, studies that focused on the DOM composition that accompany temporal hydroclimatic changes have largely focused on riverine surface water (Liu and Lu, 2019; Raymond and Saiers, 2010; Yang et al., 2013), temperate systems with perennial stream flow (Dixon et al., 2014; Osterholz et al., 2016; Powers et al., 2018), and the arctic (Rossel et al., 2020). Most estuarine and coastal DOM characterization studies have not considered inter- and intra-seasonal changes in both surface- and pore- water DOM molecular composition (Mori et al., 2019; Rossel et al., 2020) in response to extreme hydroclimatic events, such as flooding. To our knowledge, no such studies exist for semi-arid estuaries where precipitation is infrequent and riverine discharge is flashy. Further high-resolution studies of the DOM molecular composition along terrestrial to marine gradients under different hydroclimatic conditions are still necessary, especially in semi-arid estuaries.
To fill this knowledge gap, this study investigated how the DOM molecular composition varies across four seasons with different hydroclimatic conditions through the application of ultra-high performance liquid chromatography coupled to Orbitrap Fusion Tribrid mass spectrometry (UPLC-OT-FTMS). The study focused on Nueces Bay, a semi-arid region, where previous studies have shown that significant temporal and spatial variability of submarine groundwater discharge (Douglas et al., 2020; Murgulet et al., 2018) represent a source of inorganic and organic nutrients in excess of riverine inputs, which influence nutrient budgets and cycling (Douglas et al., 2021). This study sought to better constrain the influence of benthic-derived DOM inputs in relation to hydroclimatic changes through the molecular characterization and comparison of seasonal surface water and bottom sediment porewater within the estuary.
Section snippets
Study area
This study was performed in semi-arid Nueces Bay, Texas. Nueces Bay, located on the south Texas Gulf Coast, is contiguous to Corpus Christi Bay in the Nueces Estuary system (Fig. 1). The area is characterized by dry to sub-humid climates with annual precipitation averages around 76.2 cm and an average evaporation rate of 145 cm (Ockerman, 2001; Shafer, 1968). Due to low precipitation in the watershed as well as dams and diversions on the river, Nueces River discharge into the bay is typically
Environmental characterization
This study began at the end of one of the strongest multi-year (4–5 years) droughts on record for the state of Texas (Murgulet et al., 2017, Texas Water Development Board, 2018). During the drought preceding this study, Nueces Bay had become a reverse estuary with salinities as high as 38 in the bay compared to 35 of typical seawater. Furthermore, the salinities in the lower Nueces River had steadily climbed to ~16 in low-flow fall and winter 2014 (Table S1, Fig. S1), indicating negligible
DOM and nutrient dynamics
DOM dynamics in the coastal ocean are often linked to surface water riverine inputs (Chen et al., 2007; Ejarque et al., 2017); however, submarine groundwater discharge contributes significant dissolved nitrogen to local and global coastal systems (Cho et al., 2018; Douglas et al., 2021; Slomp and Van Cappellen, 2004). Relevant to this study, companion studies found that Nueces Bay receives significant submarine groundwater discharge due to steeper hydrologic gradients closer to shore and at
Conclusions
Hydroclimatic disturbances, like flood events, greatly influence DOM composition in semi-arid estuaries by changing hydraulic gradients, groundwater residence times, and seafloor recirculation in the system. In this study, DOM molecular characterization of surface water and porewater showed significant responses to these hydrologic changes, which are shown to affect the source and processing of OM within the estuary. The results of this study indicate that: 1) changing hydroclimatic conditions
Declaration of Competing Interest
The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:
Audrey R. Douglas reports financial support was provided by Texas Sea Grant. Dorina Murgulet reports financial support was provided by Texas Sea Grant. Hussain A. N. Abdulla reports financial support was provided by National Science Foundation.
Acknowledgements
Field work would not have been possible without the help of Nicholas Spalt, Melissa Treviño, Cody Lopez, Melanie Lynch, Karen Linares, Andrew Dittmer, Bimal Gyawali, Sagar Shrestha, Akshay Chintala, and Mason Maupins (Center for Water Supply Studies, Texas A&M University-Corpus Christi). We would also like to thank the two anonymous reviewers for their detailed, insightful, and constructive comments and suggestions. Texas Sea Grant (award number: NA14OAR4170102), Texas Sea Grant GIAR (project
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Optical properties of sedimentary dissolved organic matter in intertidal zones along the coast of China: Influence of anthropogenic activities
2023, Science of the Total EnvironmentCitation Excerpt :However, relatively small-scale regions were chosen in these studies, and the properties and sources of sedimentary DOM were rarely explored on a national scale. Many studies have investigated how DOM in coastal environment changes with the variation of seasons (Zhang et al., 2022b), salinity (Letourneau et al., 2021), hydroclimate (Douglas et al., 2021), eutrophication status (Zhao et al., 2021) and tidal fluctuation (Martineac et al., 2021). Significantly, coastal watersheds with important hydrological and ecological functions support the livelihoods of about three quarters of the world's population, which are vulnerable to human disturbance (Lv et al., 2020; Paerl et al., 2013).
Submarine groundwater-derived inorganic and organic nutrients vs. mariculture discharge and river contributions in a typical mariculture bay
2022, Journal of HydrologyCitation Excerpt :In addition, the widespread phytoplankton community plays an important role in the bioavailability of NH4+ and contributes to the dynamic transformation of N, ammonium in surface water may be converted to nitrate by nitrifying bacteria/plankton, thus nitrate is not always from an external source as ammonium autochthonously produced by photooxidation of organic matter and bacteria/plankton (Middelburg and Nieuwenhuize, 2000). Meanwhile, a few studies have reported that DON was also the dominant form of N in SGD (Douglas et al., 2021a, b; Santos et al., 2021), which has the potential to reflect the serious affects by local pollution sources, such as mariculture discharge and wastewater discharge on the coastal waters. To evaluate the degree of eutrophication of surface seawater in the DSB, the data of inorganic nutrients were used to calculate the Redfield ratio (N: P: Si ratio), and the ratio diagram of Si: N and Si: P was plotted (Fig. 10c).