Temporal variations in the expression of a diatom nitrate transporter gene in coastal waters off northern Taiwan: The roles of nitrate and bacteria
Graphical abstract
Introduction
Marine diatoms account for more than 20% of global CO2 fixation and nearly 40% of marine primary production (Roberts et al., 2007). Due to their large size, diatoms are readily consumed by crustacean zooplankton. Thus, the abundance of diatoms is important for energy transfer throughout the grazing food chain (Falkowski et al., 2004). In addition, some ingested diatoms are packed into fecal pallets. The sinking carbon flux that occurs through this pathway contributes significantly to the global carbon cycle (Karl et al., 2012).
The growth rate and biomass of diatoms in marine environments are often limited by nitrogen (N), iron (Fe), or phosphorus (P). Among them, N and Fe limitations occur more frequently (Downing et al., 1999). In the utilization of nitrogenous nutrients, ammonium is the chemical form preferred by microalgae (Levasseur et al., 1993; Roopnarain et al., 2015). However, since the ammonium concentration in seawater is usually low, nitrate is still the major form that supports phytoplankton growth (Kanda et al., 1990). According to studies in higher plants, the uptake of nitrate depends on a group of nitrate transporter proteins (NRTs) that control the first step in the process of nitrogen utilization. NRT proteins include a low-affinity transporter system (LATS) and a high-affinity transporter system (HATS). The LATS consists of proteins in the NRT1/PTR family (recently renamed the NPF family), and LATS proteins are activated when the nitrate concentration is greater than 1 mM (Crawford and Glass, 1998; Galvan and Fernandez, 2001; Glass et al., 2002; Okamoto et al., 2003). On the other hand, The HATS contains the NRT2/NNP protein family (Sun and Zheng, 2015). Kinetic studies indicate that HATS proteins can be further classified into a nitrate-inducible transport system (iHATS) and a constitutively expressed system (cHATS). In Arabidopsis thaliana, cHATS and iHATS typically operate within an NO3− concentration range of 10–250 μM.
In early studies among phytoplankton, genes encoding LATS proteins were mainly reported in the genomes of green algae: Chlamydomonas reinhardtii, Ostreococcus tauri, and Micromonas spp. (Fernandez and Galvan, 2007; McDonald et al., 2010). Recently, LATS-related genes belonging to the “nitrate transporter 1/peptide transporter family (NPF)” have been reported in several species of diatoms (known as diNPFs) (Rogato et al., 2015; Santin et al., 2021). However, NPFs have been shown to recognize a broad range of substrates, which included nitrate and peptides in higher plants (Léran et al., 2014). Whether diNPFs function as a typical LATS requires further investigations of their enzymatic activity, substrate specificity, and roles in diatom nitrogen metabolism. On the other hand, genes encoding HATS proteins (NRT2 family) have also been reported in diatoms (Hildebrand and Dahlin, 2000; Kang and Rynearson, 2019). The functions of diatom HATS are better characterized via the experimental techniques of 15N uptake and nitrate induced gene expression (Smith et al., 2019).
In a transcriptomic analysis, gene expressions of 3 species of model diatoms were compared under the treatment of nitrate limitation (Bender et al., 2014). The expression levels of genes related to nitrogen utilization were affected, but a common trend was absent among species. When genes in the NRT2 family were considered separately, Bender et al. (2014) discovered that individual diatom species often contained multiple forms of Nrt2, and that, in most cases, the treatment of nitrate limitation increased the expression of these genes. An analysis of the Tara Oceans eukaryotic metatranscriptomes indicated that the mRNA abundances of certain diatom Nrt2 clades were commonly high on a global scale, but transcript abundances of the ammonium transporter gene, AMT1, were divergent across geographic regions (Busseni et al., 2019). This observation suggests that individual diatom species at different locations may contain Nrt2 genes with similar expression patterns and biological functions.
In experimentally examined diatom species, the expression levels of nitrate transporter genes are closely related to the ambient nitrogen concentrations (Kang et al., 2009). The expression of Nrt2, a nitrate transporter gene, increased slightly under nitrate-sufficient conditions and rose substantially to a much higher level under nitrogen starvation conditions. The regulation of Nrt2 is also affected by the concentration of environmental ammonium. When diatom cells take up ammonium as the nitrogen source, Nrt2 expression is severely repressed (Kang et al., 2009). Sometimes, the repressed mRNA level may become lower than the detection limit of RT-qPCR. Some other factors, such as light, temperature (Bender et al., 2012), and phytoplankton-grazer interactions (Amato et al., 2018) may also affect the regulation of NO3− and NH4+ uptake. However, nutrient manipulation experiments conducted in the East China Sea showed that diatom abundance and Nrt2 expression were closely related to nutricline depth (Kang et al., 2015). Therefore, Nrt2 expression is regarded as a useful indicator of the status of nitrogen utilization in natural populations of diatoms (Suzuki et al., 2019).
In this study, we investigated a coastal ecosystem on the western border of the northwestern Pacific Ocean to reveal the temporal variation in Nrt2 expression in a diatom, Chaetoceros cf. curvisetus. Using samples collected by a plankton net, metatranscriptomes were constructed, and sequence analysis was employed to identify dominant diatoms and Nrt2-related genes. Subsequently, the expression patterns of Nrt2 were measured by RT-qPCR with carefully designed primer pairs. By examining factors that correlated with Nrt2 expression, ecological processes leading to nitrogen stress in this diatom were discussed.
Section snippets
Cruises and sampling
Phytoplankton samples were collected in coastal waters off northern Taiwan from June 2011 to June 2013 onboard R/V Ocean Researcher II (Table S1). The sampling stations were in the vicinity of Keelung Island and were grouped into two inshore stations and one offshore station. Before May 2012, the inshore station was St. A (25.18°N, 121.78°E), and the bottom depth was approximately 39 m. After July 2012, the inshore station was moved to St. B. (25.17°N, 121.81°E), with a bottom depth of 57 m.
Hydrography and nutrient concentrations
The temperature at 5 m depth showed significant seasonal variation at both the inshore and offshore stations, with an annual range from 17 to 29 °C (Fig. 2A and B). During the study period, the temperature started to increase in April and reached a peak level between May and September. After September, the temperature gradually decreased to its lowest level in December (Fig. 2A and B).
Significant seasonal variation was also observed in the combined concentrations of nitrite and nitrate [NO2−
Temporal variations in hydrochemical parameters and diatom abundance
The surface water temperature in the coastal waters off northern Taiwan exhibited a clear seasonal pattern. High temperatures prevailed from May to August, and low temperatures were prevalent during the rest of the year. Concurrently, the concentrations of nitrate and nitrite were negatively correlated with water temperature, with low concentrations observed during the warm period (Fig. 2). This seasonal pattern is well known in the East China Sea region (Gong et al., 2003). The driving
Conclusion
To construct metatranscriptomes with sufficient Nrt2 reads, a low-nitrogen treatment is needed to induce gene expression. As a result, metatranscriptomic analysis based on a low-nitrogen treatment is an effective method of species identification and qPCR primer design for target diatoms (Fig. 4). Nutrient manipulation experiments also allow the calculation of the Log (fNrt2) index, which represents the effort made by diatom cells to produce the NRT2 protein (eq. (2)). In the coastal waters off
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
We are grateful to the captain and crew of the R/V Ocean Researcher II for their assistance and to Wan-Lynn You for nutrient measurement. This study was supported in part by research grants from the ROC Ministry of Science and Technology (NSC 101-2611-M-019-016 and MOST 109-2611-M-019-003) and in part by funds from the Center of Excellence for the Oceans, National Taiwan Ocean University.
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