Literature DB >> 31753952

16S rRNA Gene Amplicon Sequencing of Microbiota in Polybutylene Succinate Adipate-Packed Denitrification Reactors Used for Water Treatment of Land-Based Recirculating Aquaculture Systems.

Takeshi Yamada1, Masako Hamada2, Miku Nakagawa2, Nobukazu Sato3, Akinori Ando4,5, Jun Ogawa4,5, Mari Yasuda6, Tomoki Kawagishi6.   

Abstract

Information on the microbiota in polybutylene succinate adipate (PBSA)-packed denitrification reactors is limited. Here, we provide 439,817 high-quality reads of the 16S rRNA gene sequences of microbiota in PBSA-packed denitrification reactors used for land-based recirculating aquaculture. The predominant microorganisms belonged to the following families: Nocardiaceae, Chitinophagaceae, Xanthobacteraceae, Burkholderiaceae, Rhodocyclaceae, Pseudomonadaceae, Rhodanobacteraceae, and Xanthomonadaceae.
Copyright © 2019 Yamada et al.

Entities:  

Year:  2019        PMID: 31753952      PMCID: PMC6872894          DOI: 10.1128/MRA.01295-19

Source DB:  PubMed          Journal:  Microbiol Resour Announc        ISSN: 2576-098X


ANNOUNCEMENT

Biodegradable plastics act as carriers for microorganism adhesion and as electron donors in denitrification reactors for removing nitrate from land-based recirculating aquaculture systems (RAS) (1–4). Biofilms form around the biodegradable plastics packed in the denitrification reactors and contribute to biological denitrification (3, 4). However, limited information regarding the microbiota adhering to the biodegradable plastics, particularly to polybutylene succinate adipate (PBSA), is available. Here, we provide 16S rRNA gene amplicon profiles of the microbiota attached to PBSA to achieve efficient nitrate removal in PBSA-packed denitrification reactors for water treatment in RAS. PBSA-packed denitrification reactors installed in three RAS tanks (250 liters) (established in Eniwa, Japan, in 2018) discharged breeding water with a nitrate concentration of <60 mg-N·liter−1 after 93 days of operation. The three reactors were loaded with PBSA pellets (Bio-PBS; Mitsubishi Chemical Corporation, Tokyo, Japan) and continuously supplied with breeding water (Table 1). Despite the difference in feeding frequency, each RAS tank bred 20 rainbow trout (average weight per fish, 92.5 ± 1.4 g) (Table 1). The sludge samples adhering to PBSA pellets were collected with the pellets from each reactor. DNA from the samples was extracted with a bead-beating method using 1-mm zirconia beads (5) and then purified according to a previous method (5). The V4 region of the 16S rRNA gene was amplified using Blend Taq polymerase (Toyobo, Osaka, Japan) and the 515F/806R primer set (6), with the following PCR conditions: 25 cycles of denaturation at 95°C for 30 s, annealing at 50°C for 30 s, and extension at 72°C for 30 s. Sequencing libraries of PCR products for each sample were prepared with three biological replicates, and sequences were determined using a MiSeq instrument and a MiSeq reagent kit v2 (2 × 300 bp; Illumina, San Diego, CA, USA) at the Bioengineering Lab. Co., Ltd. (Kanagawa, Japan). Low-quality sequences were removed using Sickle v1.33 with the following parameters: -q 20 and -l 40 (7). High-quality paired-end reads were merged using PEAR v0.9.10 with default settings (8), and then sequences were selected by SeqKit v0.8.0 with the parameters -m 245 and -M 260 (9). Selection of operational taxonomic units (OTUs) and assignment of appropriate taxa were performed using a closed-reference OTU-picking script in QIIME v1.9.1 (10) and the SILVA database (release 132) with 97% identity (11). Relative abundances of representative OTUs (>1%), summed at the family level, are shown in Fig. 1, and the indices to assess diversity were calculated with all of the selected high-quality reads for samples by QIIME v1.9.1 (11) (Table 1).
TABLE 1

Summary of 16S rRNA gene amplicon profiles of microbiota in bioreactors

Analysis measureData by sample:
SKMS_3 denitrification reactorSKMS_5 denitrification reactorSKMS_6 denitrification reactor
SRA run no.DRR186126DRR186128DRR186123DRR186125DRR186120DRR186122
Reactor vol (liters)0.782.342.34
PBSA amt (kg)133
Feeding frequencyTwice per dayTwice in 2 daysTwice per day
Breeding water temp (°C)14–1614–1614–16
Sampling date2 October 20182 October 20182 October 2018
Diversity
    Estimated sample coverage0.990.990.99
    No. of OTUs356.3673.0901.7
    Shannon diversity2.804.183.94
    Simpson diversity0.700.820.78
    Chao1 estimator662.81,129.81,475.7
    ACEb estimator653.51,181.91,459.1
    No. of high-quality reads92,893133,017213,907

Polybutylene succinate adipate (PBSA)-packed denitrification reactors.

ACE, abundance-based coverage estimator.

FIG 1

Relative abundances of microbiota in the three PBSA-packed denitrification reactors after 93 days of operation. Relative abundances (>1%) of the microbiota at the family level are displayed in a bubble plot.

Summary of 16S rRNA gene amplicon profiles of microbiota in bioreactors Polybutylene succinate adipate (PBSA)-packed denitrification reactors. ACE, abundance-based coverage estimator. Relative abundances of microbiota in the three PBSA-packed denitrification reactors after 93 days of operation. Relative abundances (>1%) of the microbiota at the family level are displayed in a bubble plot. A total of 439,817 high-quality reads were finally obtained from the three analyzed samples. Prominent microorganisms were classified into the families Nocardiaceae, Chitinophagaceae, Xanthobacteraceae, Burkholderiaceae, Rhodocyclaceae, Pseudomonadaceae, Rhodanobacteraceae, and Xanthomonadaceae. These data provide basic microbial information to achieve efficient operation of the PBSA denitrification reactor for water treatment of land-based RAS.

Data availability.

The 16S rRNA gene sequence data set has been deposited in the NCBI Sequence Read Archive (SRA) under accession number DRP005307 and SRA run accession numbers DRR186120 to DRR186128.
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