ABSTRACT
To better understand the microbial communities that drive microbiologically influenced corrosion (MIC), we characterized the bacterial communities present on various surfaces in tanks containing either petroleum-based Navy F76 diesel (F76) or hydro-processed renewable diesel (HRD) collected at the U.S. Naval Research Laboratory, Stennis Space Center, MS, USA.
KEYWORDS: microbiologically influenced corrosion, corrosion, microbiome, diesel
ANNOUNCEMENT
Fuels in storage tanks are susceptible to microbial intrusion from environmental fungi and bacteria that can result in fuel contamination and microbiologically influenced corrosion (MIC) of the tank material (1). Understanding how to mitigate MIC and which taxa affect MIC requires understanding which taxa are present. Additionally, the shift toward the use of renewable diesel derived from organic material rather than from petroleum sources may increase potential microbial challenges (2). To begin to understand these differences, we investigated the bacterial component of these communities in two fuel tanks: one containing petroleum-based Navy F76 diesel (F76) and one containing hydro-processed renewable diesel (HRD).
We sampled two fuel tanks at the U.S. Naval Research Laboratory, Stennis Space Center, MS, USA. The samples collected in these tanks are described in Table 1. We extracted DNA from samples with the ZymoBIOMICS DNA Microprep Kit (Zymo; D4301) following the standard protocol. For floating mat and excess material samples, we also extracted DNA using the DNeasy PowerBiofilm Kit (Qiagen; 24000-50). We used a one-step amplicon library preparation with V4–V5 primers (515F-Y [5′-GTGYCAGCMGCCGCGGTAA]; 926R [5′-CCGYCAATTYMTTTRAGTTT]) (3) and Thermo Phusion High-Fidelity PCR Mastermix. Some samples were re-run on two other Illumina lanes (“_2” in Table 1) and were prepared using Thermo Phusion Plus PCR Mastermix and the same primers. We cleaned PCRs using an AMPure XP bead cleanup before pooling. We sequenced the pooled library on an Illumina MiSeq at Maryland Genomics to generate 2 × 300 bp (600 cycles) paired-end reads.
TABLE 1.
Description of samples taken from two fuel tanks with different types of fuel including hydro-processed renewable diesel (HRD) and petroleum-based diesel (F76)
| Tank | Fuel type | Sample date | Sample type | Filter type | Replicate | Storage temp (°C) | Sample ID | Extraction kit | Illumina lane | Library name | Reads (unfiltered) | Reads post QC | Reads post dada2 | Reads post chimera | ASVs | Relative abundance of α-proteobacteria | SRA accession |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 1 | HRD | 7/13/23 | Interface | Unknown volume (leaking manifold), 0.22 µm FGLP (hydrophobic) | A half filter | −80 | F1 | Zymo | 2 | F1_2 | 90 | 83 | 55 | 55 | 0 | 0 | SRR31601067 |
| −80 | 3 | F1 | 1,066 | 459 | 275 | 275 | 0 | 0 | SRR31601066 | ||||||||
| B half filter | −80 | F2 | Zymo | 1 | F2_2 | 71 | 63 | 58 | 58 | 0 | 0 | SRR31601054 | |||||
| −80 | 3 | F2 | 26,588 | 710 | 455 | 455 | 0 | 0 | SRR31601044 | ||||||||
| 208 mL through 0.22 µm GS filter (hydrophilic) | A quarter filter | −80 | F3 | Zymo | 1 | F3_2 | 5,459 | 5,425 | 5,348 | 5,348 | 99 | 65.44 | SRR31601052 | ||||
| −80 | 3 | F3 | 8,743 | 2,146 | 1,905 | 1,899 | 73 | 63.82 | SRR31601053 | ||||||||
| B quarter filter | −80 | F4 | Zymo | 2 | F4_2 | 4,815 | 4,785 | 4,685 | 4,685 | 102 | 61.05 | SRR31601036 | |||||
| −80 | 3 | F4 | 59,999 | 35,260 | 34,711 | 34,372 | 186 | 64.70 | SRR31601035 | ||||||||
| C quarter filter | −80 | F5 | Zymo | 2 | F5_2 | 1,131 | 1,126 | 1,075 | 1,075 | 0 | 0 | SRR31601056 | |||||
| −80 | 3 | F5 | 92,206 | 66,282 | 65,749 | 65,632 | 214 | 59.66 | SRR31601055 | ||||||||
| D quarter filter | −80 | F6 | Zymo | 2 | F6_2 | 5,850 | 5,831 | 5,740 | 5,740 | 112 | 55.07 | SRR31601065 | |||||
| −80 | 3 | F6 | 105,315 | 74,785 | 73,918 | 73,503 | 233 | 51.33 | SRR31601064 | ||||||||
| Coupon | One swab | A | −80 | F16 | Zymo | 3 | F16 | 25,963 | 19,739 | 19,166 | 19,166 | 186 | 61.16 | SRR31601063 | |||
| One swab | B | −80 | F17 | Zymo | 3 | F17 | 126,095 | 95,625 | 94,092 | 89,688 | 219 | 56.66 | SRR31601062 | ||||
| One swab | C | −80 | F18 | Zymo | 3 | F18 | 146,549 | 112,122 | 110,412 | 104,755 | 231 | 53.48 | SRR31601061 | ||||
| Swabs from coupon tower | One swab | Single sample; No replicate | 4.0 until 10/4/2023, then −80 | F46 | Zymo | 3 | F46 | 18,326 | 10,553 | 10,244 | 10,149 | 130 | 71.65 | SRR31601047 | |||
| Excess material | ~4 mL | Single sample; No replicate | 4.0 until 10/4/2023, then −80 | F48 | Qiagen | 3 | F48_Q | 170,279 | 128,701 | 126,703 | 112,145 | 228 | 63.72 | SRR31601048 | |||
| Zymo | 3 | F48 | 99,292 | 75,655 | 74,648 | 71,879 | 268 | 59.57 | SRR31601049 | ||||||||
| 2 | F76 | 7/14/23 | Interface | Unknown volume through 0.22 µm GS (hydrophilic) | A quarter filter | −80 | F23 | Zymo | 1 | F23_2 | 56,917 | 56,728 | 56,586 | 55,954 | 121 | 81.98 | SRR31601060 |
| 3 | F23 | 4,658 | 2,038 | 1,623 | 1,604 | 31 | 87.84 | SRR31601031 | |||||||||
| B quarter filter | −80 | F24 | Zymo | 1 | F24_2 | 431 | 429 | 391 | 391 | 0 | 0 | SRR31601032 | |||||
| 3 | F24 | 2,177 | 1,716 | 1,237 | 1,237 | 35 | 82.12 | SRR31601033 | |||||||||
| Floating mat | Collected by sterile serological pipette into separatory funnel where water was drained off the bottom. Mat fraction was collected into a 2 mL tube, centrifuged at 14k for 1 min, fuel layer was pipetted off the top volume 0.5–1.5 mL | B | −80 | F28 | Qiagen | 3 | F28_Q | 141,833 | 108,700 | 107,755 | 96,774 | 124 | 82.41 | SRR31601034 | |||
| Zymo | 1 | F28_2 | 53,281 | 53,075 | 52,917 | 52,384 | 90 | 90.79 | SRR31601057 | ||||||||
| 3 | F28 | 173,824 | 132,224 | 130,818 | 110,948 | 134 | 77.39 | SRR31601058 | |||||||||
| C | −80 | F29 | Qiagen | 3 | F29_Q | 139,370 | 106,530 | 105,374 | 91,587 | 125 | 73.24 | SRR31601059 | |||||
| Zymo | 1 | F29_2 | 29,962 | 29,852 | 29,736 | 29,523 | 71 | 93.60 | SRR31601037 | ||||||||
| 3 | F29 | 160,793 | 119,537 | 118,413 | 100,925 | 114 | 91.42 | SRR31601038 | |||||||||
| D | −80 | F30 | Zymo | 3 | F30 | 67,907 | 50,709 | 50,164 | 47,327 | 100 | 93.33 | SRR31601039 | |||||
| Qiagen | 3 | F30_Q | 148,248 | 113,169 | 112,125 | 98,234 | 108 | 84.70 | SRR31601040 | ||||||||
| E | −80 | F31 | Qiagen | 3 | F31_Q | 64,669 | 48,627 | 48,062 | 44,134 | 95 | 87.19 | SRR31601041 | |||||
| Zymo | 3 | F31 | 107,587 | 81,149 | 80,232 | 73,356 | 130 | 92.41 | SRR31601042 | ||||||||
| Coupon | One swab | A | −80 | F40 | Zymo | 3 | F40 | 32,596 | 23,362 | 23,055 | 21,359 | 65 | 91.37 | SRR31601043 | |||
| One swab | B | −80 | F41 | Zymo | 3 | F41 | 52,251 | 38,531 | 38,128 | 35,475 | 75 | 82.53 | SRR31601045 | ||||
| One swab | C | −80 | F42 | Zymo | 3 | F42 | 80,789 | 62,137 | 61,678 | 59,744 | 81 | 81.19 | SRR31601046 | ||||
| Excess material | 2 mL | Single sample; No replicate | −80 | F52 | Qiagen | 3 | F52_Q | 87,822 | 67,009 | 66,154 | 60,203 | 136 | 91.77 | SRR31601050 | |||
| Zymo | 3 | F52 | 215,143 | 157,972 | 156,849 | 130,552 | 140 | 93.18 | SRR31601051 |
We analyzed samples with the R statistical Software v4.4.1. Due to poor reverse read quality, we only analyzed forward reads here. We ran the dada2 pipeline in R trimming at 240 bp and increased the maxEE to 4 with dada2 v1.32.0 (4). As we had run these samples across several lanes, we merged lanes after identifying ASVs and then removed chimeric reads. We assigned taxonomy using Silva v138.1 (5). Further pre-processing of ASV tables included removing mitochondrial and chloroplast sequences and eliminating samples with fewer than 1,000 reads after processing in R using phyloseq v1.48.0 (6). Analyses included compositional diversity analyzes calculating the centered log-ratio, performing a PCA, and identifying differences among groups with adonis2 using the R-packages vegan v2.6.8 (7) and compositions v2.0.8 (8). We also examined taxa pooled at different taxonomic levels using tip_glom to examine differences at the Class and Family levels (6). All visualizations were performed in R with ggplot v3.5.1 (9).
In these analyses, we highlight differences among bacterial communities in HRD and F76 diesels. We found significant differences between the two fuel types (PERMANOVA R2 = 0.3518, P < 0.001, Fig. 1B). Notably, the taxa in HRD were more diverse, while those in F76 were dominated by the class Alphaproteobacteria, family Sphingomonadaceae. We also found differences in other families—the HRD samples had a higher relative abundance of Bacteroidia (including Chitinophagaceae and Flavobacteriaceae), and F76 samples had a higher relative abundance of Obscuribacteraceae.
Fig 1.
(A) Picture of sample collected from F76 tank showing visible black microbial mats in the reddish fuel layer and orange corrosion products at the bottom of the water layer. (B) PCA plot summarizing microbial community differences among samples. (C) Taxa plot, condensed to class indicating relative abundance of all classes within samples. (D) Taxa plot, collapsed to family showing relative abundance of all families present at ≥5% relative abundance in one sample. In (C) and (D), we have highlighted higher taxonomic levels in color and order (e.g., all blues in (C) are Proteobacteria and all blues in (D) are Alphaproteobacteria).
ACKNOWLEDGMENTS
The funding for this research was provided by the DARPA Arcadia program as part of independent verification and validation efforts performed by the U.S. Naval Research Laboratory.
Contributor Information
Jason S. Lee, Email: jason.s.lee23.civ@us.navy.mil.
Irene L. G. Newton, Indiana University Bloomington, Bloomington, Indiana, USA
DATA AVAILABILITY
All raw reads were deposited in GenBank SRA under the BioProject PRJNA1193007, and links to individual samples (SRR31601031-SRR31601067) are in Table 1.
REFERENCES
- 1. Passman FJ. 2013. Microbial contamination and its control in fuels and fuel systems since 1980 – a review. Int Biodeterior Biodegradation 81:88–104. doi: 10.1016/j.ibiod.2012.08.002 [DOI] [Google Scholar]
- 2. Stamps BW, Bojanowski CL, Drake CA, Nunn HS, Lloyd PF, Floyd JG, Emmerich KA, Neal AR, Crookes-Goodson WJ, Stevenson BS. 2020. In situ linkage of fungal and bacterial proliferation to microbiologically influenced corrosion in B20 biodiesel storage tanks. Front Microbiol 11:167. doi: 10.3389/fmicb.2020.00167 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3. Parada AE, Needham DM, Fuhrman JA. 2016. Every base matters: assessing small subunit rRNA primers for marine microbiomes with mock communities, time series and global field samples. Environ Microbiol 18:1403–1414. doi: 10.1111/1462-2920.13023 [DOI] [PubMed] [Google Scholar]
- 4. Callahan BJ, McMurdie PJ, Rosen MJ, Han AW, Johnson AJA, Holmes SP. 2016. DADA2: High-resolution sample inference from Illumina amplicon data. Nat Methods 13:581–583. doi: 10.1038/nmeth.3869 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5. McLaren MR, Callahan BJ. 2021. Silva 138.1 prokaryotic SSU taxonomic training data formatted for DADA2. Zenodo
- 6. McMurdie PJ, Holmes S. 2013. Phyloseq: an R package for reproducible interactive analysis and graphics of microbiome census data. PLoS One 8. doi: 10.1371/journal.pone.0061217 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7. Oksanen J, Simpson GL, Blanchet FG, Kindt R, Legendre P, Minchin PR, O’Hara RB, Solymos P, Stevens MHH, Szoecs E, et al. 2001. Community ecology package. vegan. doi: 10.5281/zenodo.3878538 [DOI] [Google Scholar]
- 8. Boogaart K van den, Tolosana-Delgado R, Bren M. 2024. Compositions: Compositional 92 Data Analysis (2.0-8)
- 9. Wickham H. 2016. Ggplot2: elegant graphics for data analysis. Springer International Publishing, Cham, Cham, Switzerland. [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
All raw reads were deposited in GenBank SRA under the BioProject PRJNA1193007, and links to individual samples (SRR31601031-SRR31601067) are in Table 1.

