Journal of Oceanology and Limnology   2023, Vol. 41 issue(6): 2276-2291     PDF       
http://dx.doi.org/10.1007/s00343-022-2189-8
Institute of Oceanology, Chinese Academy of Sciences
0

Article Information

XIA Pinhua, LI Guoqing, HUANG Xianfei, SHI Lei, DU Xin, LIN Tao
Temporal characteristics of algae-denitrifying bacteria co-occurrence patterns and denitrifier assembly in epiphytic biofilms on submerged macrophytes in Caohai Lake, SW China
Journal of Oceanology and Limnology, 41(6): 2276-2291
http://dx.doi.org/10.1007/s00343-022-2189-8

Article History

Received Apr. 13, 2022
accepted in principle Jul. 28, 2022
accepted for publication Sep. 21, 2022
Temporal characteristics of algae-denitrifying bacteria co-occurrence patterns and denitrifier assembly in epiphytic biofilms on submerged macrophytes in Caohai Lake, SW China
Pinhua XIA#, Guoqing LI#, Xianfei HUANG, Lei SHI, Xin DU, Tao LIN     
Guizhou Province Key Laboratory for Information System of Mountainous Areas and Protection of Ecological Environment, Guizhou Normal University, Guiyang 550001, China
Abstract: Denitrifying bacteria in epiphytic biofilms play a crucial role in nitrogen cycle in aquatic habitats. However, little is known about the connection between algae and denitrifying bacteria and their assembly processes in epiphytic biofilms. Epiphytic biofilms were collected from submerged macrophytes (Patamogeton lucens and Najas marina L.) in the Caohai Lake, Guizhou, SW China, from July to November 2020 to: (1) investigate the impact of abiotic and biotic variables on denitrifying bacterial communities; (2) investigate the temporal variation of the algae-denitrifying bacteria co-occurrence networks; and (3) determine the contribution of deterministic and stochastic processes to the formation of denitrifying bacterial communities. Abiotic and biotic factors influenced the variation in the denitrifying bacterial community, as shown in the Mantel test. The co-occurrence network analysis unveiled intricate interactions among algae to denitrifying bacteria. Denitrifying bacterial community co-occurrence network complexity (larger average degrees representing stronger network complexity) increased continuously from July to September and decreased in October before increasing in November. The co-occurrence network complexity of the algae and nirS-encoding denitrifying bacteria tended to increase from July to November. The co-occurrence network complexity of the algal and denitrifying bacterial communities was modified by ammonia nitrogen (NH4+-N) and total phosphorus (TP), pH, and water temperature (WT), according to the ordinary least-squares (OLS) model. The modified stochasticity ratio (MST) results reveal that deterministic selection dominated the assembly of denitrifying bacterial communities. The influence of environmental variables to denitrifying bacterial communities, as well as characteristics of algal-bacterial co-occurrence networks and the assembly process of denitrifying bacterial communities, were discovered in epiphytic biofilms in this study. The findings could aid in the appropriate understanding and use of epiphytic biofilms denitrification function, as well as the enhancement of water quality.
Keywords: denitrifying bacteria    epiphytic biofilms    co-occurrence networks    submerged macrophytes    community assembly    
1 INTRODUCTION

Biofilms are a complex community of microbiota (algae, bacteria, fungi, animals, and inorganic and organic detritus) that are attached to substrata (Wetzel, 1983; Gubelit and Grossart, 2020). Biofilms are widespread in soils, sediments, submerged plants, and surfaces of natural and artificial substrates and are essential for the absorption, decomposition and transformation to water pollutants (Pang et al., 2016; Han et al., 2018). The submerged plant-biofilm system absorbs approximately 30% of the ammonia nitrogen and removes more than 50% of the ammonia nitrogen by denitrification in constructed wetland mesocosms (Mu et al., 2020). Exceptional capacity for denitrification of epiphytic bacterial communities in natural aquatic ecosystems uses functional predictive analysis (Yan et al., 2019). Epiphytic biofilms therefore play an important function within the nitrogen cycle in aquatic ecological systems (Mu et al., 2020; Li et al., 2022).

Denitrifying functional microorganisms drive denitrification in ecosystems. Microorganisms release enzymes such as nitrate reductase (Nar), nitrite reductase (Nir), nitric oxide reductase (Nor), nitrite reductase (Nir), nitric oxide reductase (Nor), and nitrous oxide reductase (Nos) that catalyze the denitrification process (Fozia et al., 2020). Nitrite reductase (nirS and nirK) are functionally equivalent but structurally separate restriction enzymes in denitrification that mediate the conversion of nitrite (NO2-) to nitric oxide (NO) (Kraft et al., 2011; Shrewsbury et al., 2016; Chen et al., 2017). The nirS and nirK functional genes have been widely used to research denitrifying bacteria in sediments (Zheng et al., 2015; Hong et al., 2019), soil (Wang et al., 2019), compost (Zhong et al., 2020), wastewater (Lu et al., 2014), and biofilms (Vila-Costa et al., 2014; Zhang et al., 2020). Temperature (Zhou et al., 2016), pH (Liu et al., 2010; Yang et al., 2017), nitrate-nitrogen (NO3--N) (Shi et al., 2019; Dai et al., 2020), carbon to nitrogen ratio (C꞉N) (Dai et al., 2020), total nitrogen (TN) (Zhou et al., 2016), dissolved oxygen (DO) (Shi et al., 2019), and ammonia-nitrogen (NH4+-N) (Zhou et al., 2016; Shi et al., 2019; Dai et al., 2020) all affect the community composition, abundance, and diversity of nirS- and nirK-type denitrifying bacteria. In addition, adding algae can be very effective in enhancing the effectiveness of denitrification in artificial wetlands (Cheng et al., 2021). The genes of the nirS and the nirK and their relationship with environmental factors in submerged plant biofilms were investigated (Lyautey et al., 2013; Vila-Costa et al., 2014; Yan et al., 2018; Zhang et al., 2020). However, previous research has overlooked the association with algal and denitrifiers in epiphytic biofilms.

There are intricate relationships among the algae and bacteria, such as metabolism, competition, and parasitism (Natrah et al., 2014). Algae can release oxygen and secrete organic matter or dead residues as a nutrient source to promote bacterial growth (Natrah et al., 2014). Algae may also secrete antagonistic substances to kill bacteria or compete for nutrient deficiencies (Desbois et al., 2008; Natrah et al., 2014). Moreover, algae can secrete carbon source substances to promote denitrification (Ishida et al., 2008; Lu et al., 2014), and there may be complex interactions between algae and denitrifying bacteria. Co-occurrence network analysis, in which nodes represent species and links represent interactions between species, is widely used to study the interactions between microbial communities and their responses on environmental variations (Wang et al., 2021; Yu et al., 2021; Liu et al., 2022). As a result, co-occurrence network analysis opens up new avenues for research into the interaction between algal and denitrifying bacterial communities.

The primary factors of microbial community assembly in aquatic habitats are deterministic and stochastic processes. Non-random, ecological niche-based mechanisms such as environmental filtering and diverse biological interactions between community species are examples of deterministic processes (e.g., competition, facilitation, metabolism, and predation) (Niederdorfer et al., 2021). Birth, death, dispersal, and migration are the key factors that drive microbial community assembly in stochastic processes (Zhou and Ning, 2017). The construction of microbial communities appears to be regulated by both deterministic and stochastic mechanisms (Zhou and Ning, 2017). Environmental filtration, interspecies interactions, and dispersion limitation all influence microbial co-occurrence patterns (D'Amen et al., 2018; Liu et al., 2022). Thus, to study on the mechanism of denitrifying bacterial community assembly is helpful to understand the algae-denitrifying bacteria co-occurrence patterns and correlation in epiphytic biofilms.

We studied the biofilm attached to typical submerged plants (Patamogeton lucens and Najas marina L.) using high-throughput sequencing technologies and statistical analysis to: (1) determine the effect of abiotic and biotic variables on the denitrifying bacterial communities; (2) investigate the temporal variation of the algae-denitrifying bacteria co-occurrence networks; and (3) identify the contribution of deterministic and stochastic processes to the formation of denitrifying bacterial communities.

2 MATERIAL AND METHOD 2.1 Study area and sampling

The research site is located on the Caohai Lake (104°12′E–104°18′E, 26°49′N–26°53′N) in Guizhou Province, SW China (Supplementary Fig.S1). This area has a subtropical humid monsoon climate with an average annual temperature of 10.5 ℃ and 1 000 mm of precipitation (Xia et al., 2020). Submerged macrophytes (Patamogeton lucens, Najas marina L.) and water were collected at six sites in July, August, September, October, and November of 2020.

All plant samples were taken in triplicates from three to five plants of each submerged macrophyte and transferred to sterile 500-mL polyethylene bottles containing 400 mL of 50-mmol/L phosphate-buffered saline (PES, pH=7.4) solution, stored with ice bags, and returned to the laboratory rapidly (Zhang et al., 2016; Xia et al., 2020). For water chemistry analysis, water samples (1.5 L) were taken from the surface water in the sampling region.

2.2 Sample pretreatment

After 3 min of ultrasonic treatment in a KQ5200 DE ultrasonic cleaner bath (Kunshan Ultrasonic Instruments Manufacture Co. Ltd., Kunshan, China), 30 min in a SHZ-82A thermostatic shaking water bath (225 r/min) (Jintan Ronghua Instrument Manufacture Co. Ltd., Jiangsu, China), and another 3 min of ultrasonic treatment (Zhang et al., 2016; Xia et al., 2020). 100 mL of mixed liquor was filtered through 0.22-μm membrane filters (Millipore Ireland Ltd., Ireland) after complete detachment for gather epiphytic denitrifiers (Yan et al., 2019). The filters were gathered and kept at 20 ℃ until the DNA was extracted.

Take out the leaves and lay them flat on a graduated glass plate, place them in the light for photography and finally calculate the leaf area (Song et al., 2019). The eluate was kept in 100 mL of formaldehyde solution (3%), then algae were accounted for and identified using phytoplankton atlas under the light microscope (Yan et al., 2019). The algal density was then calculated from the above data. The pH and water temperature (WT) of the overlying water were measured by a potable meter. Standard methods in China for assessing surface water were used to quantify total nitrogen (TN), total phosphorus (TP), ammonia (NH4+-N), chemical oxygen demand (CODMn, using the potassium permanganate method), and chlorophyll a (Chl a). Secchi disc was used to test water transparency (SD).

2.3 DNA extraction and Illumina MiSep high-throughput sequencing

According to the manufacturer's instructions, microbial DNA was extracted from filters using a FastDNA® Spin Kit for Soil (MPBiomedicals, Santa Ana, CA, USA). DNA concentration was checked using a NanoDrop2000 and (Thermo Fisher Scientific, Waltham, MA, USA), and DNA quality was assessed by performing 1% agarose gel electrophoresis according to the manufacturer's instructions. For PCR amplification analysis, DNA samples were kept at -80 ℃. To investigate the microbial community composition of nirK- and nirS-encoding denitrifiers in epiphytic biofilms on submerged macrophytes, the nirK gene was amplified using primers (F1aCu: 5′-ATCATGGTSCTGCCGCG-3′/R3Cu: 5′-GCCTCGA TCAGRTTGTGGTT-3′) and the nirS gene was amplified using primers (the 20-L PCR reaction mixture contains 4 L of 5X FastPfu Buffer, 0.8 mL of each primer (5 μm), 10 ng of template DNA, 0.4 mL of FastPfu polymerase, 0.2 mL of BSA, 2 mL of 2.5 mmol/L dNTPs, and 20 mL of ddH2O). After that, the PCR products were purified, and libraries were created. An Illumina MiSeq platform was used for sequencing (Illumina, San Diego, USA).

2.4 Statistical analysis

ArcGIS was used to create the sampling diagram (version 10.6). In this work, we used "Hellinger" to transform microbial community data and log(x+1) to transform physicochemical data (excluding pH). R (version 4.0.1, https://www.r-project.org/) was used to examine physicochemical data for the water column from different month in significance of differences using nonparametric tests (Kruskal-Wallis test and Wilcoxon test). Boxplots were used to depict the physico-chemical properties of the surface water, which were created in R using the "ggplot2" package (Xia et al., 2020).

The algal composition and algal density data in the epiphytic biofilm were processed with Excel software and visualized with Hiplot (https://hiplot.com.cn/). The community's alpha diversity was measured using the Chao 1 index, Shannon index, Simpson index, and phylogenetic diversity (PD) index, all of which were calculated using the R package "vegan". The "aov" function in R was used to examine the substantial differences (P < 0.05) in alpha diversity index of the denitrifying bacterial communities between different months using one-way analysis of variance (one-way ANOVA).

The principal coordinate analysis (PCoA) and permutation multivariate analysis of variance (PERMANOVA) based on Bray-Curtis distances at the denitrifying bacteria OTU level were implemented in "vegan" installation package in R, and in "ggplot2" package in R for visualization, to study the differences in denitrifying bacteria community in different months. Bray-Curtis distances at the denitrifying bacteria OTU level were implemented in the "vegan" installation package in R, and the "ggplot2" package in R for visualization, to study the differences in denitrifying bacteria community in different months. The "core" function in the "corrplot" package in R was used to compute and plot the Spearman correlation between physicochemical data and algal density in epiphytic biofilms. Using the "vegan" package in R, the Mantel test was used to investigate the association between denitrifying bacterial community composition and abiotic and biotic variables.

The co-occurrence network analysis was used to evaluate the interaction between denitrifiers and algae in epiphytic biofilms, and it was processed using the "WGCNA" package in R based on relative abundance of denitrifying bacteria and algal data, and then visualized with Gephi (V0.9.2) software. For the analysis, the best ordinary least squares (OLS) multiple regression models of variance in the complexity of the co-occurrence network of algae with nirS-type denitrifier and the network of the co-occurrence network of algae with nirK-type denitrifier were chosen. Using "MASS" packages in R, the adequacy of the models was assessed using Akaike's information criterion (AIC), and the variance inflation factor (VIF) was determined using "CAR" packages in R. The niche breadth index and Modified stochasticity ratio (MST), which were generated using the "spaa" and "NST" packages in R, respectively, were used to analyze the relative importance of stochasticity and determinism for denitrifying community assembly.

3 RESULT 3.1 Physicochemical property

In different months, the physicochemical properties of the water body were examined (Supplementary Fig.S2). The water temperature gradually decreased from July to November, and there were significant differences in different months (P < 0.05). From July to September, total phosphorus (TP), ammonia nitrogen (NH4+-N), and pH values decreased, then increased in November. The Chl-a content and transparency (SD) were not significantly different between months.

3.2 Algae and denitrifying bacteria community composition and diversity

The algae in the epiphytic biofilms were identified, and 6 phylum and 77 genera of algae were obtained. The dominant phylum of algae in epiphytic biofilms were Chlorophyta (51.37%), Bacillariophyta (20.67%), and Cyanophyta (20.56%) (Fig. 1). The density of algae in the epiphytic biofilms was 1.33×107 cells/cm2 (August), 3.54×106 cells/cm2 (October), 2.80×106 cells/cm2 (July), 2.19×106 cells/cm2 (November), and 1.62×106 cells/cm2 (September) in descending order (Supplementary Fig.S3).

Fig.1 The relative abundance of algae in epiphytic biofilms at the phylum

The dominate phylum of nirS-type and nirK-type denitrifying bacteria were Proteobacteria (39.98%± 19.64% and 51.50%±14.29%, respectively) and unclassified bacteria (51.86%±17.14% and 45.36%± 13.74%, respectively) (Fig. 2). In different months, the Shannon, Simpson, Chao1, and PD indices of the nirS-type denitrifying bacteria community varied significantly (P < 0.05) (Table 1). From July through November, the Shannon index exhibited an upward trend (Table 1). At different month, the Simpson, Chao1, and PD indices of the nirK-type denitrifying bacterial community were not significantly different (Table 1).

Fig.2 The relative abundance of denitrifying community in epiphytic biofilms at the phylum
Table 1 The alpha diversity of nirS- and nirK-encoding bacteria in the epiphytic biofilms
3.3 Relationships between denitrifying bacteria and abiotic and biotic factors

The nirS-type denitrifying bacteria differed significantly (R2=0.134, P=0.02) during different months, according to PCoA and PERMANOVA analyses based on the Bray-Curtis distances (Fig. 3). The nirS-type denitrifying bacteria' s beta diversity was highest in August, and significantly higher (P < 0.05) in July–September than in October–November (Fig. 3c). The Mantel test demonstrated a significantly positive association with the CODMn, Chl a, SD, WT, Cyanophyta density, and total algal density (R > 0.1, P < 0.05) and a strong link with the nirS-type denitrifying bacteria and Euglenophyta density (R=0.215, P=0.002) (Fig. 3d).

Fig.3 The principal coordinate analysis (PCoA) of nirS- and nirK-encoding denitrifier at OTU level (calculated using Bray-Curtis) (a & b); the beta-diversity were estimated based on a Bray-Curtis distance matrix (c); correlations among physicochemical properties, algae (phyla) density and the composition of the denitrifying community in epiphytic biofilms (d) In (c), significant differences among the month are indicted by different letters (P < 0.05); in (d), pairwise comparisons of physicochemical properties and algal density are displayed with a color gradient to denote Spearman's correlation coefficients. Asterisks indicate significant correlations: *: P < 0.05; **: P < 0.01; ***: P < 0.001. CODMn: chemical oxygen demand; TP: total phosphorus; TN: total nitrogen; NH4+-N: ammonia nitrogen; Chl a: chlorophyll a; SD: water transparency; WT: water temperature; Cya: Cyanophyta; Bac: Bacillariophyta; Pry: Pryrophyta; Eug: Euglenophyta; Chr: Chrysophyta; Chl: Chlorophyta; TAB: total algae biomass.

The PCoA and PERMANOVA analyses showed that the nirK-type denitrifying bacteria differed significantly (R2=0.160, P=0.01) at the different month (Fig. 3). The largest beta diversity was found in nirK-type denitrifying bacteria in September, which was significantly greater than in August, October, and November (P < 0.05) (Fig. 3c). The Mantel test found a significant correlation between the nirK-type denitrifying bacteria and Chl a (R=0.158, P < 0.05) (Fig. 3d), and no significant correlation with other environmental factors.

3.4 Co-occurrence network

The denitrifying bacterial community characteristics in epiphytic biofilms were assessed using co-occurrence network analysis at different months (Supplementary Fig.S4). From July to September, the nirS-type denitrifying bacterial community co-occurrence network had increasing links and an average degree, then decreased in October before reaching its maximum nodes, links, and average degree in November (Supplementary Table S1). From July to September, the nodes, links, and average degree of the nirK-type denitrifying bacterial community co-occurrence network risen substantially and then decreased in October, with the links and average degree increasing in November, but the maximum number of nodes, links, and average degree appearing in September (Supplementary Table S1). Although the co-occurrence patterns of nirS- and nirK-type denitrifying bacteria showed similar temporal variation, the periods when the highest average degree occurred were different. The average degree of co-occurrence network of the nirK-type denitrifying bacterial community was higher than the nirS-type denitrifying bacteria community except in November.

The nirS- and nirK-type denitrifying bacteria (OTU level) and algae (genus level) from epiphytic biofilms at different months were used to create co-occurrence networks (Figs. 45). The links of the nirS-type denitrifying bacteria and algae co-occurrence network in the biofilm from the July to the November showed an increasing trend and reached a maximum in the November (Fig. 4). The average degree of the nirK-type denitrifying bacteria and algae co-occurrence network tended to increase from the July to the October, reaching a maximum in the October and decreasing to a minimum in the November (Fig. 5). From July to October, the nirK-type denitrifying bacteria and algae co-occurrence network had a higher average degree than the nirS-type denitrifying bacteria and algae co-occurrence network (Table 2).

Fig.4 The association network of nirS-encoding denitrifiers and algae The red lines represent positive correlations and green lines represent negative correlations (abs(r) > 0.6, P < 0.05).
Fig.5 The association network of nirK-encoding denitrifiers and algae The red lines represent positive correlations and green lines represent negative correlations (abs(r) > 0.6, P < 0.05).
Table 2 The properties of the network co-occurrence of nirS-type and nirK-type denitrifying bacteria with algae in different months

The WT, TP, CODMn, NH4+-N, and pH explained 95.2% of the variation in the complexity of the nirS-type denitrifying bacteria and algae co-occurrence network (Supplementary Table S2), while the WT, TP, TN, CODMn, NH4+-N, and pH explained 70.8% to the complexity by the nirK-type denitrifying bacteria with algae co-occurrence network (Supplementary Table S2), according to the ordinary least-squares (OLS) model.

3.5 Microbial community assembly process

Niche breadths were used to investigate the contributions of deterministic and stochastic processes within denitrifying bacterial community. In July, the nirS-type denitrifying bacteria's niche breadth was significantly higher than in August, September, and October (P < 0.05) (Fig. 6). The nirK-type denitrifying bacteria's niche breadth was significantly higher in November than in July (P < 0.05), and the niche breadth of the nirK-type denitrifying bacteria was increasing trend by month (Fig. 6). The MST was used to analyze the dominant processes in microbial community construction. The MST mean values for the nirS- and nirK-type denitrifying bacterial communities were both below the 50% cut-off value, indicating a greater contribution from deterministic processes (Fig. 7). Furthermore, the mean MST of nirS-type denitrifying bacteria and nirK-type denitrifying bacteria has been increasing trend by month (Fig. 7).

Fig.6 Boxplots showing the mean habitat niche breadth nirS- and nirK-type denitrifier in epiphytic biofilms Significant differences among the month are indicted by different letters (P < 0.05).
Fig.7 Barplots showing the comparison of modified stochasticity ratio (MST) of nirS- and nirK-type denitrifier in epiphytic biofilms Significant differences among the month as indicted by different letters (P < 0.05).
4 DISCUSSION 4.1 Effect of abiotic and biotic factors on denitrifying bacterial communities

Previous research has suggested that temperature can affect bacterial and algal dynamics in aquatic ecosystems either directly or indirectly (Wang et al., 2015; Xia et al., 2020). Because different species are subject different suitable growth and reproduction temperature. In our study, the abiotic factors (CODMn, SD, and WT) and biotic factors (Cyanophyta density, Euglenophyta density, total algae density, and Chl a) and were significantly associated with nirS-type denitrifying bacteria communities (Fig. 3). The nirK-type denitrifying bacteria were only significantly correlated with Chl a, and no other environmental factors were found to be significant (Fig. 3). This indicates that the change of denitrifying bacteria community is closely related to the change of environmental factors. In addition, it was found that the variation of denitrifying bacteria community was not only related to the changes of physical and chemical factors, but also significantly related to the density of algae. Carbon sources, which are thought to be a key factor influencing the function and structure of denitrifying bacterial community (Lu et al., 2014; Zhou et al., 2016) and have a greater impact on denitrifying bacterial community structure compared to those of other factors (e.g., carbon to nitrogen ratio, C꞉N) (Lu et al., 2014). Denitrifying bacteria require organic carbon as an electron donor during cell growth and denitrification, and the addition of carbon sources can effectively promote cell growth and improve denitrification efficiency (Rajta et al., 2020). Different carbon sources such as glycerol, glucose, succinate, ethanol, sucrose, methanol, formic acid, and sodium pyruvate have been tested for their effects on denitrification rates (Rajta et al., 2020). Thus, the growth of denitrifying bacteria in aquatic ecosystems may be extremely dependent on the carbon sources secreted by algae. This may be the reason why the denitrifying bacteria community is significantly correlated with algal density.

In aquatic ecosystems, Cyanophyta fix organic carbon and synthesize and secrete extracellular organic matter (EOM) such as polysaccharides, proteins, and nucleic acids through photosynthesis, and EOM can be used directly as a carbon source to promote heterotrophic bacteria's growth (Henderson et al., 2008; Ramanan et al., 2015). The abundance of denitrifying bacteria increased significantly under moderate cyanobacterial blooms, and denitrification rates increased (Henderson et al., 2008; Deng et al., 2020), producing large amounts of EOM to supply denitrifying bacteria to facilitate the denitrification process. Cyanophyta carbon secretion is affected by external environmental changes; for example, elevated light intensity can significantly increase extracellular polysaccharide production in Anabaena (Moreno et al., 1998). Enhancing the proportion of polysaccharide substances in EOM can effectively promote denitrification (Chen et al., 2018). Furthermore, apoptotic Cyanophyta can be employed as a heterotrophic bacterial carbon source to encourage heterotrophic bacterial development (Natrah et al., 2014; Deng et al., 2020). Bacterial enzyme production is promoted by algae in unidentified bacterial biofilms under light (Espeland et al., 2001; Natrah et al., 2014). Chlorophyll a has good biocatalytic and electron transfer effects and can effectively promote nitrite reduction during denitrification (Lu et al., 2020). The lack of carbon source material in artificial wetlands can lead to reduced denitrification, and the addition of algae can be very effective in improving denitrification efficiency in artificial wetlands (Cheng et al., 2021).

In conclusion, the abiotic and biotic factors in our study had an important influence on the structure of denitrifying bacterial communities. In epiphytic biofilms on submerged macrophytes, there may be complicated interactions between algae and denitrifying bacteria.

4.2 Temporal variation of algae-denitrifying bacteria co-occurrence network

Microbial interactions and microbial community succession are frequently studied using co-occurrence network analysis (Jeong et al., 2016; Liu et al., 2020). Network analysis reveals the complex relationship between algae and bacteria and is dominated by positive correlations (Xia et al., 2020). In our study, the denitrifying bacteria community variation is closely related to abiotic and biotic factors, especially denitrifying bacteria and algae may have complex interactions. As a result, co-occurrence network analysis was utilized to investigate the interaction between algae and denitrifying bacteria in epiphytic biofilms, as well as their temporal alterations.

Saikia et al. (2013) concluded that biofilm formation consists of four stages: (1) nutrients are adsorbed on the solid surface following physicochemical processes; (2) bacteria begin to colonize and produce extracellular organic matter (EPS); (3) protozoa, algae, and other microorganisms colonize; and (4) eukaryotes begin to colonize and have nutritional and grazing functions. The second stage is where it starts to be defined as a biofilm. We collected algae and denitrifying bacteria in July, indicating that the biofilm has formed. The early stage of biofilm (July) in our study showed less microbial growth and weaker species interactions as compared those of the other month. The network complexity of the July to September of the nirS- and nirK-type denitrifying bacteria in the biofilm had an increasing trend. It was indicated a continuous colonization of the biofilm by microorganisms, an increase in species competition relationships, and the beginning of a large number of intra- and interspecific co-occurrence relationships (Niederdorfer et al., 2021). The network complexity decreased in the October, which was probably because the core community was gradually forming, with only transient new species attaching and migrating (Niederdorfer et al., 2021). The increase in network complexity during the November indicates that stable microbial communities were formed in the biofilm, and microbial interactions were enhanced. In our study, the co-occurrence network of the nirS-type denitrifying bacterial communities during the biofilm from July to November was less complex and more modular compared to the co-occurrence network of the nirK-type denitrifying bacterial communities (Table 2). The nirS-type denitrifying bacteria associated more closely with each other than the nirK-type denitrifying bacteria, implying that higher co-occurrence network complexity indicated greater microbial interactions.

The difference in modularity may be due to ecological niche differentiation, habitat heterogeneity, or diversity selection (Li et al., 2021). Ecological studies have found the coexistence of specific species of algae and bacteria with specific interactions between them (Kouzuma and Watanabe, 2015). Algae and bacteria have complicated relationships that include metabolism, competition, and parasitism (Natrah et al., 2014). Organic matter secreted by algae sustains bacterial growth, whereas bacteria consume oxygen to release carbon dioxide to promote algal growth (Liu et al., 2017). Bacteria degrade organic matter while producing vitamin B12, an extracellular secretion necessary for algal growth (Natrah et al., 2014). In addition, some microalgal metabolites have bactericidal effects, such as green algal proteins, against both Gram-positive and Gram-negative bacteria (Gonçalves et al., 2017). Co-occurrence networks can be effective in uncovering potential algal-bacterial relationships, and biofilms as new life forms are ideal materials for studying temporal changes in algal-bacterial relationships. The links of the algae and nirS-type denitrifying bacteria co-occurrence network in our study from the July to the November increased, and the network complexity showed an increasing trend (Fig. 4). Planktonic microorganisms constantly colonize biofilms in aquatic ecosystems, and some microorganisms return to the aquatic environment because of unsuitable growth (He et al., 2014). Along with the enhanced interaction between biofilm-growing algae and denitrifying bacteria, more microorganisms colonize the biofilm. Positive and negative interactions between microbial species in co-occurrence networks are considered to be reciprocal and antagonistic relationships (Miao et al., 2021). In our study, there was a tendency for a positive correlation between algae and denitrifying bacteria (positive links > 60%), which was probably because algae secrete carbon sources to promote the growth of denitrifying bacteria, forming a reciprocal relationship (Lu et al., 2014; Natrah et al., 2014). In the October, the highest percentage of negative correlation edges between the nirS-type denitrifying bacteria and algal interaction networks indicated a large number of antagonistic relationships. This is because algae compete with bacteria for nutrient deficiency or secrete antagonistic substances to inhibit bacterial growth (Natrah et al., 2014). The complexity of the nirK-type denitrifying bacteria and algal co-occurrence network increased continuously from the July phase to the October, with enhanced microbial interactions. The lowest network complexity in the November period may be because algae associated with the nirK-type denitrifying bacteria are affected by seasonal changes.

Interaction patterns between algae and bacteria are not constant and are influenced by a variety of environmental factors and multiple interactions (Zhu et al., 2021). The algal-bacterial relationships and co-occurrence network complexity in our study were dynamic with the biofilm growth and were influenced by the external environment. Contaminants such as heavy metals, nanomaterials, and pesticides can affect algal-bacterial interactions (You et al., 2021). Under nutrient-limited conditions, heterotrophic bacteria may compete with Cyanophyta for nutrient salts such as nitrogen and phosphorus. Seasonal changes in algal community composition and biomass in epiphytic biofilms are characterized and significantly influenced by the WT, pH, and nutrients (Feng et al., 2011), thus affecting changes in the algal-bacterial network relationships. Our results suggest that changes in the nitrogen and phosphorus nutrients, pH, and temperature can affect changes in the complexity of the denitrifying bacteria-algae co-occurrence network.

4.3 Denitrifying community assembly in biofilms is dominated by deterministic processes

The niche-based theory and neutral theory are two significant complimentary methods for understanding microbial community building, and they are widely applied in diverse environments (Chen and Wen, 2021; Xiong et al., 2021). The sediment community in hot spring sediments had a stronger phylogenetic clustering and was predominantly directed by heterogeneous selection, whereas the water community was primarily governed by undominated stochastic processes and dispersal constraints (He et al., 2021). The formation of bacterial and archaeal community in subtropical riverine systems is strongly affected by deterministic and stochastic processes, but the stochastic process of bacterial communities is much more pronounced than that of archaeal communities (Wang et al., 2020). In the surface soil of a typical red soil critical zone, stochastic mechanisms dominate the bacterial community assembly process, but deterministic processes dominate in the deeper layers (Wu et al., 2020). Under Spartina alterniflora invasion, stochastic processes drive the formation of archaeal and bacterial communities in sediments, with bacteria having a higher relative stochastic influence than archaea (Chen and Wen, 2021). In the Hanhe River, spatial factors (stochastic processes) explain more of the composition of the bacterioplankton community than environmental factors, with neutral community models explaining most of the fall and spring community variation, and the structure of the bacterioplankton community is largely influenced by stochastic processes (Sun et al., 2021). Microorganisms in these environments are not only controlled by deterministic factors and environmental conditions that control community construction but also by stochastic processes such as birth, death, colonization, and species formation. Deterministic processes dominate bacterial community development in epiphytic biofilms, although stochastic processes' effects rose significantly in months later than June (He et al., 2020).

Based on niche breadth and MST, we investigated the assembly process of nirS- and nirK-type denitrifying bacteria in biofilms. As a metric of stochasticity, the MST value reflects the contribution of the stochastic assembly relative to the deterministic assembly. The mean MST of the nirS- and nirK-type denitrifying bacterial communities was found to be below the 50% cut-off limit, showing that deterministic processes dominated the nirS- and nirK-type denitrifying bacteria. The deterministic process of the nirS-type denitrifying bacterial communities contributed the most in August, followed by the stochasticity process, which steadily grew. The contribution of the stochasticity process of the nirK-type denitrifying bacterial communities in July to October has increased the trend and decreased in November. This shows that the ecological process of the denitrifying bacteria in epiphytic biofilms is driven by the season.

In microorganisms, the nirS and nirK genes are mutually exclusive, and bacteria with one or the other gene may have ecological niche differentiation (Jones and Hallin, 2010). We evaluated the niche breadth of the denitrifying bacterial communities and discovered that the nirS-type denitrifying bacteria had much more niche breadth than the nirK-type denitrifying bacteria. Organisms having a wider niche range may have more metabolic flexibility and are less impacted by deterministic processes (Chen et al., 2021), implying that the nirK-type bacteria are more susceptible to environmental filtering than the nirS-type denitrifying bacteria (Li et al., 2021). Deterministic processes based on the traditional ecological niche theory suggest that deterministic factors (e.g., species traits and interspecific interactions such as competition, predation, mutually beneficial symbiosis, and trade-offs) and environmental conditions (e.g., pH, temperature, salinity, and moisture) control community construction (Zhou and Ning, 2017). The contribution of deterministic processes to the community assembly of nirK-type denitrifying bacteria was higher than that of nirS-type denitrifying bacteria (Supplementary Fig.S5); thus, interspecific interactions and interactions with algae were stronger in the nirK-type denitrifying bacteria than in the nirS-type denitrifying bacteria. The assembly processes of the nirS-type and nirK-type denitrifying bacteria in the biofilms were dominated by deterministic mechanisms, which were driven by the season.

5 CONCLUSION

The community structure and co-occurrence network of nirS- and nirK-type denitrifying bacteria epiphytic biofilms were studied in this study and found to be different in different months (July to November). The organization and composition of denitrifying bacterial communities are influenced by algal density and physicochemical variables. The co-occurrence network complexity of nirS- and nirK-type denitrifying bacteria changed in a similar pattern. The algae and nirS-type denitrifying bacteria co-occurrence network complexity in epiphytic biofilms tended to increase from the July to the November, while the algae and nirK-type denitrifying bacteria co-occurrence network complexity tended to increase, and then decrease. Both genotypes were dominated by deterministic processes in community assembly, with the nirS-type denitrifying bacteria having a larger ecological niche, larger MST, and higher migration rate than the nirK-type denitrifying bacteria. Our results provide new perspectives on the influence of algae on denitrifying bacterial communities, algal-bacterial relationship succession, and denitrifying bacterial community assembly. Moreover, findings from this study could be used for the proper understanding and utilization of the denitrification function of epiphytic biofilms and the improvement of water environment quality.

6 DATA AVAILABILITY STATEMENT

The data that support the findings of this study are available from the corresponding author upon reasonable request.

Electronic supplementary material

Supplementary material (Supplementary Figs.S1–S5 and Tables S1–S2) is available in the online version of this article at https://doi.org/10.1007/s00343-022-2189-8.

References
Chen J, Ying G G, Liu Y S, et al. 2017. Nitrogen removal and its relationship with the nitrogen-cycle genes and microorganisms in the horizontal subsurface flow constructed wetlands with different design parameters. Journal of Environmental Science and Health, Part A-Toxic/Hazardous Substances & Environmental Engineering, 52(8): 804-818. DOI:10.1080/10934529.2017.1305181
Chen Q L, Hu H W, Yan Z Z, et al. 2021. Deterministic selection dominates microbial community assembly in termite mounds. Soil Biology & Biochemistry, 152: 108073. DOI:10.1016/j.soilbio.2020.108073
Chen W D, Wen D H. 2021. Archaeal and bacterial communities assembly and co-occurrence networks in subtropical mangrove sediments under Spartina alterniflora invasion. Environmental Microbiome, 16: 10. DOI:10.1186/s40793-021-00377-y
Chen X C, Huang Y Y, Chen G Q, et al. 2018. The secretion of organics by living Microcystis under the dark/anoxic condition and its enhancing effect on nitrate removal. Chemosphere, 196: 280-287. DOI:10.1016/j.chemosphere.2017.12.197
Cheng S, Huai J, Zhong F, et al. 2021. Enhancing denitrification in constructed wetland with algae addition. Environmental Science and Pollution Research, 29: 1949-1960. DOI:10.1007/s11356-021-15755-9
Dai H T, Zhu R B, Sun B W, et al. 2020. Effects of sea animal activities on tundra soil denitrification and nirS- and nirK-encoding denitrifier community in maritime Antarctica. Frontiers in Microbiology, 11: 573302. DOI:10.3389/fmicb.2020.573302
D'Amen M, Mod H K, Gotelli N J, et al. 2018. Disentangling biotic interactions, environmental filters, and dispersal limitation as drivers of species co-occurrence. Ecography, 41(8): 1233-1244. DOI:10.1111/ecog.03148
Deng J, Chen X C, Huang Y Y, et al. 2020. Biogeochemical cycling processes associated with cyanobacterial aggregates. Acta Microbiologica Sinica, 60(9): 1922-1940. (in Chinese with English abstract) DOI:10.13343/j.cnki.wsxb.20200201
Desbois A P, Lebl T, Yan L M, et al. 2008. Isolation and structural characterisation of two antibacterial free fatty acids from the marine diatom, Phaeodactylum tricornutum. Applied Microbiology and Biotechnology, 81(4): 755-764. DOI:10.1007/s00253-008-1714-9
Espeland E M, Francoeur S N, Wetzel R G. 2001. Influence of algal photosynthesis on biofilm bacterial production and associated glucosidase and xylosidase activities. Microbial Ecology, 42(4): 524-530. DOI:10.1007/s00248-001-1022-8
Feng J, Wang F, Xie S L. 2011. Structure and dynamics of the periphytic algae of Jinyang Lake in Shanxi Province, North China. Acta Ecologica Sinica, 31(6): 310-316. DOI:10.1016/j.chnaes.2011.07.003
Fozia N, Zheng Y L, Hou L J, et al. 2020. Community dynamics and activity of nirS-harboring denitrifiers in sediments of the Indus River Estuary. Marine Pollution Bulletin, 153: 110971. DOI:10.1016/j.marpolbul.2020.110971
Gonçalves A L, Pires J C M, Simões M. 2017. A review on the use of microalgal consortia for wastewater treatment. Algal Research, 24: 403-415. DOI:10.1016/j.algal.2016.11.008
Gubelit Y I, Grossart H P. 2020. New methods, new concepts: what can be applied to freshwater periphyton?. Frontiers in Microbiology, 11: 1275. DOI:10.3389/fmicb.2020.01275
Han B, Zhang S H, Zhang L S, et al. 2018. Characterization of microbes and denitrifiers attached to two species of floating plants in the wetlands of Lake Taihu. PLoS One, 13(11): e0207443. DOI:10.1371/journal.pone.0207443
He D, Ren L J, Wu Q L. 2014. Contrasting diversity of epibiotic bacteria and surrounding bacterioplankton of a common submerged macrophyte, Potamogeton crispus, in freshwater lakes. FEMS Microbiology Ecology, 90(3): 551-562. DOI:10.1111/1574-6941.12414
He D, Ren L, Wu Q L. 2020. Growing season drives the compositional changes and assembly processes of epiphytic bacterial communities of two submerged macrophytes in Taihu Lake. Fems Microbiology Ecology, 96(4): fiaa025. DOI:10.1093/femsec/fiaa025
He Q, Wang S, Hou W G, et al. 2021. Temperature and microbial interactions drive the deterministic assembly processes in sediments of hot springs. Science of the Total Environment, 772: 145465. DOI:10.1016/j.scitotenv.2021.145465
Henderson R K, Baker A, Parsons S A, et al. 2008. Characterisation of algogenic organic matter extracted from cyanobacteria, green algae and diatoms. Water Research, 42(13): 3435-3445. DOI:10.1016/j.watres.2007.10.032
Hong P, Wu X Q, Shu Y L, et al. 2019. Denitrification characterization of dissolved oxygen microprofiles in lake surface sediment through analyzing abundance, expression, community composition and enzymatic activities of denitrifier functional genes. AMB Express, 9(1): 129. DOI:10.1186/s13568-019-0855-9
Ishida C K, Arnon S, Peterson C G, et al. 2008. Influence of algal community structure on denitrification rates in periphyton cultivated on artificial substrata. Microbial Ecology, 56(1): 140-152. DOI:10.1007/s00248-007-9332-0
Jeong S Y, Yi T, Lee C H, et al. 2016. Spatiotemporal dynamics and correlation networks of bacterial and fungal communities in a membrane bioreactor. Water Research, 105: 218-230. DOI:10.1016/j.watres.2016.09.001
Jones C M, Hallin S. 2010. Ecological and evolutionary factors underlying global and local assembly of denitrifier communities. The ISME Journal, 4(5): 633-641. DOI:10.1038/ismej.2009.152
Kouzuma A, Watanabe K. 2015. Exploring the potential of algae/bacteria interactions. Current Opinion in Biotechnology, 33: 125-129. DOI:10.1016/j.copbio.2015.02.007
Kraft B, Strous M, Tegetmeyer H E. 2011. Microbial nitrate respiration-Genes, enzymes and environmental distribution. Journal of Biotechnology, 155(1): 104-117. DOI:10.1016/j.jbiotec.2010.12.025
Li C C, Wang L F, Ji S P, et al. 2021. The ecology of the plastisphere: microbial composition, function, assembly, and network in the freshwater and seawater ecosystems. Water Research, 202: 117428. DOI:10.1016/j.watres.2021.117428
Li G Q, Yan D B, Xia P H, et al. 2022. Community structure and assembly of denitrifying bacteria in epiphytic biofilms in a freshwater lake ecosystem. Journal of Oceanology and Limnology, 40(3): 1039-1050. DOI:10.1007/s00343-021-1084-z
Liu B B, Mørkved P T, Frostegård Å, et al. 2010. Denitrification gene pools, transcription and kinetics of NO, N2O and N2 production as affected by soil pH. FEMS Microbiology Ecology, 72(3): 407-417. DOI:10.1111/j.1574-6941.2010.00856.x
Liu J Z, Wu Y H, Wu C X, et al. 2017. Advanced nutrient removal from surface water by a consortium of attached microalgae and bacteria: a review. Bioresource Technology, 241: 1127-1137. DOI:10.1016/j.biortech.2017.06.054
Liu S W, Yu H, Yu Y H, et al. 2022. Ecological stability of microbial communities in Lake Donghu regulated by keystone taxa. Ecological Indicators, 136: 108695. DOI:10.1016/j.ecolind.2022.108695
Liu Y S, Gong L X, Mu X Y, et al. 2020. Characterization and co-occurrence of microbial community in epiphytic biofilms and surface sediments of wetlands with submersed macrophytes. Science of the Total Environment, 715: 136950. DOI:10.1016/j.scitotenv.2020.136950
Lu C C, Xie Z, Guo J B, et al. 2020. Chlorophyll as natural redox mediators for the denitrification process. International Biodeterioration & Biodegradation, 148: 104895. DOI:10.1016/j.ibiod.2020.104895
Lu H J, Chandran K, Stensel D. 2014. Microbial ecology of denitrification in biological wastewater treatment. Water Research, 64: 237-254. DOI:10.1016/j.watres.2014.06.042
Lyautey E, Hallin S, Teissier S, et al. 2013. Abundance, activity and structure of denitrifier communities in phototrophic river biofilms (River Garonne, France). Hydrobiologia, 716(1): 177-187. DOI:10.1007/s10750-013-1561-2
Miao L Z, Wang C Q, Adyel T M, et al. 2021. Periphytic biofilm formation on natural and artificial substrates: comparison of microbial compositions, interactions, and functions. Frontiers in Microbiology, 12: 684903. DOI:10.3389/fmicb.2021.684903
Moreno J, Vargas M A, Olivares H, et al. 1998. Exopolysaccharide production by the cyanobacterium Anabaena sp. ATCC 33047 in batch and continuous culture. Journal of Biotechnology, 60(3): 175-182. DOI:10.1016/S0168-1656(98)00003-0
Mu X Y, Lv X Y, Liu W, et al. 2020. Biofilms attached to Myriophyllum spicatum play a dominant role in nitrogen removal in constructed wetland mesocosms with submersed macrophytes: evidence from 15N tracking, nitrogen budgets and metagenomics analyses. Environmental Pollution, 266: 115203. DOI:10.1016/j.envpol.2020.115203
Natrah F M I, Bossier P, Sorgeloos P, et al. 2014. Significance of microalgal-bacterial interactions for aquaculture. Reviews in Aquaculture, 6(1): 48-61. DOI:10.1111/raq.12024
Niederdorfer R, Fragner L, Yuan L, et al. 2021. Distinct growth stages controlled by the interplay of deterministic and stochastic processes in functional anammox biofilms. Water Research, 200: 117225. DOI:10.1016/j.watres.2021.117225
Pang S, Zhang S H, Lv X Y, et al. 2016. Characterization of bacterial community in biofilm and sediments of wetlands dominated by aquatic macrophytes. Ecological Engineering, 97: 242-250. DOI:10.1016/j.ecoleng.2016.10.011
Rajta A, Bhatia R, Setia H, et al. 2020. Role of heterotrophic aerobic denitrifying bacteria in nitrate removal from wastewater. Journal of Applied Microbiology, 128(5): 1261-1278. DOI:10.1111/jam.14476
Ramanan R, Kang Z, Kim B H, et al. 2015. Phycosphere bacterial diversity in green algae reveals an apparent similarity across habitats. Algal Research, 8: 140-144. DOI:10.1016/j.algal.2015.02.003
Saikia S K, Nandi S, Majumder S. 2013. A review on the role of nutrients in development and organization of periphyton. Journal of Research in Biology, 3(1): 780-788.
Shi R J, Xu S M, Qi Z H, et al. 2019. Seasonal patterns and environmental drivers of nirS- and nirK-encoding denitrifiers in sediments of Daya Bay, China. Oceanologia, 61(3): 308-320. DOI:10.1016/j.oceano.2019.01.002
Shrewsbury L H, Smith J L, Huggins D R, et al. 2016. Denitrifier abundance has a greater influence on denitrification rates at larger landscape scales but is a lesser driver than environmental variables. Soil Biology & Biochemistry, 103: 221-231. DOI:10.1016/j.soilbio.2016.08.016
Song X, Lin T, Xia P H, et al. 2019. Algae composition and accumulation characteristics of heavy metals in epiphytic bioflioms of submerged macrophytes. Journal of Lake Sciences, 31(5): 1268-1278. DOI:10.18307/2019.0523
Sun H, Pan B Z, He H R, et al. 2021. Assembly processes and co-occurrence relationships in the bacterioplankton communities of a large river system. Ecological Indicators, 126: 107643. DOI:10.1016/j.ecolind.2021.107643
Vila-Costa M, Bartrons M, Catalan J, et al. 2014. Nitrogen-cycling genes in epilithic biofilms of oligotrophic high-altitude lakes (Central Pyrenees, Spain). Microbial Ecology, 68(1): 60-69. DOI:10.1007/s00248-014-0417-2
Wang B H, Stirling E, He Z L, et al. 2021. Pollution alters methanogenic and methanotrophic communities and increases dissolved methane in small ponds. Science of the Total Environment, 801: 149723. DOI:10.1016/j.scitotenv.2021.149723
Wang H L, Han J Q, Deng N, et al. 2019. Effects of the natural restoration time of abandoned farmland in a semiarid region on the soil denitrification rates and abundance and community structure of denitrifying bacteria. Applied Microbiology and Biotechnology, 103(4): 1939-1951. DOI:10.1007/s00253-018-09575-0
Wang Y M, Liu L M, Chen H H, et al. 2015. Spatiotemporal dynamics and determinants of planktonic bacterial and microeukaryotic communities in a Chinese subtropical river. Applied Microbiology and Biotechnology, 99(21): 9255-9266. DOI:10.1007/s00253-015-6773-0
Wang Y M, Pan J, Yang J, et al. 2020. Patterns and processes of free-living and particle-associated bacterioplankton and archaeaplankton communities in a subtropical river-bay system in South China. Limnology and Oceanography, 65(S1): S161-S179. DOI:10.1002/lno.11314
Wetzel R G. 1983. Periphyton of Freshwater Ecosystems. Springer, Växjö, Sweden, https://doi.org/10.1007/978-94-009-7293-3.
Wu H Y, Adams J M, Shi Y, et al. 2020. Depth-dependent patterns of bacterial communities and assembly processes in a typical red soil critical zone. Geomicrobiology Journal, 37(3): 201-212. DOI:10.1080/01490451.2019.1688432
Xia P H, Yan D B, Sun R G, et al. 2020. Community composition and correlations between bacteria and algae within epiphytic biofilms on submerged macrophytes in a plateau lake, southwest China. Science of the Total Environment, 727: 138398. DOI:10.1016/j.scitotenv.2020.138398
Xiong C, Zhu Y G, Wang J T, et al. 2021. Host selection shapes crop microbiome assembly and network complexity. New Phytologist, 229(2): 1091-1104. DOI:10.1111/nph.16890
Yan D B, Xia P H, Song X, et al. 2019. Community structure and functional diversity of epiphytic bacteria and planktonic bacteria on submerged macrophytes in Caohai Lake, southwest of China. Annals of Microbiology, 69(9): 933-944. DOI:10.1007/s13213-019-01485-4
Yan L Y, Zhang S H, Lin D, et al. 2018. Nitrogen loading affects microbes, nitrifiers and denitrifiers attached to submerged macrophyte in constructed wetlands. Science of the Total Environment, 622-623: 121-126. DOI:10.1016/j.scitotenv.2017.11.234
Yang Y D, Zhao J, Jiang Y, et al. 2017. Response of bacteria harboring nirS and nirK genes to different N fertilization rates in an alkaline northern Chinese soil. European Journal of Soil Biology, 82: 1-9. DOI:10.1016/j.ejsobi.2017.05.006
You X Q, Xu N, Yang X, et al. 2021. Pollutants affect algae-bacteria interactions: a critical review. Environmental Pollution, 276: 116723. DOI:10.1016/j.envpol.2021.116723
Yu H, Liu X Y, Yang C, et al. 2021. Co-symbiosis of arbuscular mycorrhizal fungi (AMF) and diazotrophs promote biological nitrogen fixation in mangrove ecosystems. Soil Biology and Biochemistry, 161: 108382. DOI:10.1016/j.soilbio.2021.108382
Zhang S H, Pang S, Wang P F, et al. 2016. Responses of bacterial community structure and denitrifying bacteria in biofilm to submerged macrophytes and nitrate. Scientific Reports, 6(1): 36178. DOI:10.1038/srep36178
Zhang Z Q, Chen H Z, Mu X Y, et al. 2020. Nitrate application decreased microbial biodiversity but stimulated denitrifiers in epiphytic biofilms on Ceratophyllum demersum. Journal of Environmental Management, 269: 110814. DOI:10.1016/j.jenvman.2020.110814
Zheng Y L, Hou L J, Liu M, et al. 2015. Diversity, abundance, and distribution of nirS-harboring denitrifiers in intertidal sediments of the Yangtze Estuary. Microbial Ecology, 70(1): 30-40. DOI:10.1007/s00248-015-0567-x
Zhong X Z, Zeng Y, Wang S P, et al. 2020. Insight into the microbiology of nitrogen cycle in the dairy manure composting process revealed by combining high-throughput sequencing and quantitative PCR. Bioresource Technology, 301: 122760. DOI:10.1016/j.biortech.2020.122760
Zhou J Z, Ning D L. 2017. Stochastic community assembly: does it matter in microbial ecology?. Microbiology and Molecular Biology Reviews, 81(4): e00002-17. DOI:10.1128/mmbr.00002-17
Zhou S L, Huang T L, Zhang C H, et al. 2016. Illumina MiSeq sequencing reveals the community composition of NirS-Type and NirK-Type denitrifiers in Zhoucun reservoir-A large shallow eutrophic reservoir in northern China. RSC Advances, 6(94): 91517-91528. DOI:10.1039/c6ra18017e
Zhu J M, Zhou J, Wang H, et al. 2021. The ecological network approach to algal-bacterial relationships: review and prospects. Chinese Science Bulletin, 66(34): 4378-4394. DOI:10.1360/TB-2021-0314