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Concentration and Distribution of Oligochaeta Worms in the Waters of Kejapanan, Pasuruan, Indonesia Polluted by Mercury Waste using DNA Barcode
Corresponding Author(s) : Moh. Awaludin Adam
Jurnal Ilmiah Perikanan dan Kelautan, 2024: IN PRESS ISSUE (JUST ACCEPTED MANUSCRIPT, 2024)
Abstract
Graphical Abstract
Higlight Research
- Based on AAS test, results showed that the St2 sample has the highest concentration of mercury compared to other locations. St2 samples are samples taken right at the pollutant source.
- The results showed that the samples consist of the Nadidae family with two species, namely Limnodrilus hoffmeisteri and Branchiura sowerbyi.
- The COI gene that was successfully amplified had a length of approximately 700 bp using a 3000 bp DNA ladder as a comparison.
- Based on the results of the SEM-EDX test, the worm samples contained several elements. The majority of them are organic except Al, Si, and Ti. Aluminium (Al), Silicon (Si), and Titanium (Ti) are metals that are used by organisms.
Abstract
Physiological monitoring of mercury waste contamination can be carried out using the biota around the waters. This study aims to identify concentration of Hg and the types of worms in the waters of Kejapanan, Pasuruan, East Java with a molecular approach. Target gene amplification was carried out using the mitochondrial genome COI barcode primer. Analysis of molecular identification was performed with DNA analysis and phylogenetic, similarity, DNA sequence variation, genetic distance, and the BOLD System. The concentration Hg was analyzed using AAS and the distribution of mercury in the worms was analyzed using SEM Edax Mapping. The results showed that the pollutant source area (St2 sample) has the highest concentration of mercury compared to other locations. The results of molecular identification indicate the formation of two clusters. The amplified samples produced DNA bands according to the target (600-700 bp), and the process was continued with morphological-based-key identification. The results showed that they consist of the family Nadidae with two species, namely Limnodrilus hoffmeisteri and Branchiura sowerbyi. A DNA length of 709 bp as well as nucleotide composition. BLAST results showed that species L. hoffmeisteri and B. sowerbyi had similarity indexes of 99% and 86%, respectively. Based on the research results, it was found that there was an accumulation of mercury exposure in worms in polluted areas. For this reason, the results of this study can provide a novelty that worms can be used as biomonitoring of water pollution using the barcode data.
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References
Adam, M. A., Maftuch, M., Kilawati, Y., & Risjani, Y. (2019a). Detection of metallothionein protein biomarkers (MTs) and pinocytosis activity in gambusia fish (Gambusia affinis) exposed to cadmium. Nature Environment and Pollution Technology, 18(3):989-994.
Adam, M. A., Maftuch, M., Kilawati, Y., & Risjani, Y. (2019b). The effect of cadmium exposure on the cytoskeleton and morphology of the gill chloride cells in juvenile mosquito fish (Gambusia affinis). Egyptian Journal of Aquatic Research, 45(4):337-343.
Adam, M. A., Maftuch, M., Kilawati, Y., & Tahirah, S. N. (2018). Analysis of heavy metal pollutant in wangi river Pasuruan and its impact on Gambusia affinis. Jurnal Pembangunan dan Alam Lestari, 9(2):120-128.
Adam, M. A., Soegianto, A., Melissa, C., Khumaidi, A., Ramli, R., Ernawati, E., Mei, I., & Insivitawati, E. (2022). CD4 cell activation with the CD8 marker and metallothionein expression in the gills of cadmium-exposed mosquito fish (Gambusia affinis Baird and Girard 1853) juveniles. Emerging Contaminants, 8(1):280-287.
Ahmed, M. S., Chowdhury, M. M. K., & Nahar, L. (2019). Molecular characterization of small indigenous fish species (SIS) of Bangladesh through DNA barcodes. Gene, 684(1):53-57.
Ali, F. S., Ismail, M., & Aly, W. (2020). DNA barcoding to characterize biodiversity of freshwater fishes of Egypt. Molecular Biology Reports, 47(8):5865-5877.
Aly, W., & Abouelfadl, K. Y. (2020). Impact of low-level water pollution on some biological aspects of redbelly tilapia (Coptodon zillii) in River Nile, Egypt. Egyptian Journal of Aquatic Research, 46(3):273-279.
Anggorowati R. D., Deni N. E. & Listyorini, D. (2019). DNA barcoding of introduced typical fishes in Telaga Sari, Pasuruan Regency. Biotropika: Journal of Tropical Biology, 7(2):51-62.
Anggraini, P., Asikin, A. N., & Kusumaningrum, I. (2022). Effect of liquid smoke concentration on chemical and organoleptic characteristics of baung fish (Mystus gulio) smoke. [in English]. Media Teknologi Hasil Perikanan, 10(1):60-67.
ATSDR (Agency for Toxic Substances and Disease Registry). (2022). Toxicological profile for mercury. In U.S. Department of Health and Human Services (Issue April).
Barregard, L., Fabricius-Lagging, E., Lundh, T., Mölne, J., Wallin, M., Olausson, M., Modigh, C., & Sallsten, G. (2010). Cadmium, mercury, and lead in kidney cortex of living kidney donors: Impact of different exposure sources. Environmental Research, 110(1):47-54.
Beauchamp, K. A., Kathman, R. D., McDowell, T. S., & Hedrick, R. P. (2001). Molecular phylogeny of tubificid oligochaetes with special emphasis on Tubifex tubifex (Tubificidae). Molecular Phylogenetics and Evolution, 19(2):216-224.
Becker, M., König, S., & Hoppe, B. (2021). A simple PCR-based approach for rapid detection of Ips typographus and Ips duplicatus in the presence of (associated) symbionts and parasites. Journal of Plant Diseases and Protection, 128(2):527-534.
Bird, G. J., & Ladle, M. (1981). Aspects of the morphology and ecology of two British tubificids (Oligochaeta). Journal of Zoology, 194(4):493-504.
Blakemore, R. J., Lee, W., Ryu, J.-S., Ahn, M. H., & Kim, S. R. (2012). Accidental vaginal parasitism by oligochaete worms (Annelida: Oligochaeta). Opuscula Zoologica-Budapest, 43(2):197-201.
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Cheng, D., Song, J., Zhao, X., Wang, S., Lin, Q., Peng, J., Su, P., & Deng, W. (2019). Effects of chironomid larvae and Limnodrilus hoffmeisteri bioturbation on the distribution and flux of chromium at the sediment-water interface. Journal of Environmental Management, 245:151-159.
Christoffersen, M. L. (2012). Phylogeny of basal descendants of cocoon-forming annelids (Clitellata). Turkish Journal of Zoology, 36(1):95-119.
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DeSalle, R., & Goldstein, P. (2019). Review and interpretation of trends in DNA Barcoding. Frontiers in Ecology and Evolution, 7(302):1-11.
Devos, E., Devos, P., & Cornet, M. (1998). Effect of cadmium on the cytoskeleton and morphology of gill chloride cells in parr and smolt Atlantic salmon (Salmo salar). Fish Physiology & Biochemistry, 18:15-27.
Elsaied, H., Soliman, T., Siam, R., Saad Abdelkarim, M., & Sonbol, S. (2022). Differential rRNA gene metabarcoding of prokaryotic consortia in desert athalassohaline and thalassohaline brines. Egyptian Journal of Aquatic Research, 48(3):223-231.
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Folmer, O., Black, M., Hoeh, W., Lutz, R., & Vrijenhoel, R. (1994). DNA primers for amplification of mitochondrial cytochrome c oxidase subunit I from diverse metazoan invertebrates. Molecular Marine Biology and Biotechnology, 3(5):294-299.
Geller, J., Meyer, C., Parker, M., & Hawk, H. (2013). Redesign of PCR primers for mitochondrial cytochrome c oxidase subunit I for marine invertebrates and application in all-taxa biotic surveys. Molecular Ecology Resources, 13(5):851-861.
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Government Regulation. (2001). Republic of Indonesia Government Regulation Number 82 of 2001 on management of water quality and control over water pollution. [in English]. Republic of Indonesia Government.
Hebert, P. D. N., Cywinska, A., Ball, S. L., & DeWaard, J. R. (2003). Biological identifications through DNA barcodes. Proceedings of the Royal Society B: Biological Sciences, 270(1):313-321.
Hikam, A. M., Mubarakati, N. J., Dailami, M., & Toha, A. H. A. (2021). DNA barcoding in marine invertebrates. [in English]. Jurnal Biologi Udayana, 25(1):46-56.
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Klerks, P. L., & Bartholomew, P. R. (1991). Cadmium accumulation and detoxification in a Cd-resistant population of the oligochaete Limnodrilus hoffmeisteri. Aquatic Toxicology, 19(2):97-112.
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Kumar, D. (2012). Role of non-enzymatic antioxidants in stimulation of metallothionein against metal toxicity. International Journal of Environmental Sciences, 2(3):1596-1604.
Lee, J. W., Choi, H., Hwang, U. K., Kang, J. C., Kang, Y. J., Kim, K. Il, & Kim, J. H. (2019). Toxic effects of lead exposure on bioaccumulation, oxidative stress, neurotoxicity, and immune responses in fish: A review. Environmental Toxicology and Pharmacology, 68(1):101-108.
Lee, J. Y., Tokumoto, M., Hwang, G. W., Kim, M. S., Takahashi, T., Naganuma, A., Yoshida, M., & Satoh, M. (2018). Effect of metallothionein-III on mercury-induced chemokine gene expression. Toxics, 6(3):1-9.
Liu, Y., Fend, S. V., Martinsson, S., & Erséus, C. (2017). Extensive cryptic diversity in the cosmopolitan sludge worm Limnodrilus hoffmeisteri (Clitellata, Naididae). Organisms Diversity and Evolution, 17(2):477-495.
Macirella, R., & Brunelli, E. (2017). Morphofunctional alterations in zebrafish (Danio rerio) gills after exposure to mercury chloride. International Journal of Molecular Sciences, 18(4):1-19.
Maktoof, A. A (2020). Use of two plants to remove pollutants in wastewater in constructed wetlands in Southern Iraq. Egyptian Journal of Aquatic Research, 46(3):227-233.
Mao, L., Liu, C., Lu, K., Su, Y., Gu, C., Huang, Q., & Petersen, E. J. (2016). Exposure of few layer graphene to Limnodrilus hoffmeisteri modifies the graphene and changes its bioaccumulation by other organisms. Carbon, 109(1):566-574.
Naveed, M. I. (2012). Preliminary studies on aquatic Oligochaeta in and around Chennai, Tamil Nadu, India. Turkish Journal of Zoology, 36(1), 25–37.
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