Physicochemical Characterization and Water Quality Feasibility across Three Source Water Types in the Ciputat Area, South Tangerang

Authors

  • Vetty Megantari Department of Chemistry, Faculty of Science and Technology, Universitas Islam Negeri Syarif Hidayatullah Jakarta, Jl. Ir. H. Juanda No. 95, Ciputat, South Tangerang 15412, (Indonesia) https://orcid.org/0000-0003-3205-2748
  • Nurul Amilia Department of Chemistry, Faculty of Science and Technology, Universitas Islam Negeri Syarif Hidayatullah Jakarta, Jl. Ir. H. Juanda No. 95, Ciputat, South Tangerang 15412, (Indonesia) https://orcid.org/0009-0001-2842-7423
  • Nita Rosita Department of Chemistry, Faculty of Science and Technology, Universitas Islam Negeri Syarif Hidayatullah Jakarta, Jl. Ir. H. Juanda No. 95, Ciputat, South Tangerang 15412, (Indonesia) https://orcid.org/0000-0003-3987-3397
  • Wahyu Permata Department of Chemistry, Faculty of Science and Technology, Universitas Islam Negeri Syarif Hidayatullah Jakarta, Jl. Ir. H. Juanda No. 95, Ciputat, South Tangerang 15412, (Indonesia)
  • Fitriah Hatiningsih Department of Chemistry, Faculty of Science and Technology, Universitas Islam Negeri Syarif Hidayatullah Jakarta, Jl. Ir. H. Juanda No. 95, Ciputat, South Tangerang 15412, (Indonesia)

DOI:

https://doi.org/10.47352/jbrnt.2964-0431.456

Keywords:

physicochemical, tap water, water quality, water refill station

Abstract

This study aims to characterize the physicochemical quality and assess the water quality feasibility across three source Water Source Type used in parallel within the Ciputat area, South Tangerang, namely tap water from public facilities and residential areas (Type I, n = 4), tap water from university buildings at Universitas Islam Negeri Syarif Hidayatullah Jakarta (Type II, n = 8), and drinking water from refill stations (Type III, n = 8), evaluated against the Ministry of Health Regulation (Permenkes) No. 2 of 2023. In situ parameters included pH, temperature, dissolved oxygen (DO), turbidity, total dissolved solids (TDS), and salinity. Laboratory analyses encompassed iron (Fe) and manganese (Mn) determination via atomic absorption spectrophotometry (AAS) across all three Water Source Types, as well as ammonia (N-NH3) and phosphate (P-PO4) analysis using UV-Vis spectrophotometry specifically for Water Source Types II and III. The results indicated that the turbidity of all samples (3.70–23.81 NTU) exceeded the maximum permissible limit of less than 3 NTU across all three water sources. Whereas, based on the WHO guideline, drinking water turbidity should not exceed 5 NTU [1]. The campus tap water was dominated by acidic pH levels (5.40–7.50), with six out of eight buildings falling below the minimum threshold of 6.5. Iron levels in all samples were below the method detection limit, whereas manganese levels exceeded the quality standard of 0.1 mg/L exclusively in Water Source Type I (0.336–0.853 mg/L), which is consistent with geogenic sources in shallow groundwater. The N-NH3 and P-PO4 concentrations in all samples complied with the specific parameter standards of Permenkes No. 2 of 2023. In conclusion, no matrix satisfied all parameters simultaneously. Hence, corrective interventions must be tailored to the dominant characteristics of each respective water source.

References

[1]     WHO, UNICEF, Progress on Household Drinking Water, Sanitation and Hygiene 2000–2020: Five Years into the SDGs, World Health Organization, Geneva, 2021.

[2]     J. Irianto, et al., Household Drinking Water Quality Study Report (SKAM-RT) 2020, Ministry of Health of the Republic of Indonesia, Jakarta, 2021.

[3]     N. Pertiwi, et al., Environmental Laboratory Parameters, PT Global Eksekutif Teknologi, Padang, 2023. Available at: www.globaleksekutifteknologi.co.id.

[4]     A. Kappler, C. Bryce, M. Mansor, U. Lueder, J.M. Byrne, E.D. Swanner, An evolving view on biogeochemical cycling of iron, Nat. Rev. Microbiol. 19 (2021) 360–374. https://doi.org/10.1038/s41579-020-00502-7.

DOI: https://doi.org/10.1038/s41579-020-00502-7

[5]     J.E. Tobiason, A. Bazilio, J. Goodwill, X. Mai, C. Nguyen, Manganese removal from drinking water sources, Curr. Pollut. Rep. 2 (2016) 168–177. https://doi.org/10.1007/s40726-016-0036-2.

DOI: https://doi.org/10.1007/s40726-016-0036-2

[6]     United Nations Environment Programme (UNEP), A Snapshot of the World's Water Quality: Towards a Global Assessment, UNEP, Nairobi, 2016. Available at: www.unep.org.

[7]     J.T. Bunce, E. Ndam, I.D. Ofiteru, A. Moore, D.W. Graham, A review of phosphorus removal technologies and their applicability to small-scale domestic wastewater treatment systems, Front. Environ. Sci. 6 (2018). https://doi.org/10.3389/fenvs.2018.00008.

DOI: https://doi.org/10.3389/fenvs.2018.00008

[8]     M. Demlie, E. Hingston, Z. Mnisi, A study of the sources, human health implications and low-cost treatment options of iron-rich groundwater in the northeastern coastal areas of KwaZulu-Natal, South Africa, J. Geochem. Explor. 144 (2014) 504–510. https://doi.org/10.1016/j.gexplo.2014.05.011.

DOI: https://doi.org/10.1016/j.gexplo.2014.05.011

[9]     N.N. Rudi, et al., A review on manganese sources, occurrences, negative impacts, and potential treatment using adsorption process, Int. J. Emerg. Trends Eng. Res. 8 (2020) 233–247. https://doi.org/10.30534/ijeter/2020/3381.22020.

DOI: https://doi.org/10.30534/ijeter/2020/3381.22020

[10]   World Health Organization, Guidelines for Drinking-Water Quality: Fourth Edition Incorporating the First and Second Addenda, WHO, Geneva, 2022.

[11]   T.M. Edwards, H.J. Puglis, D.B. Kent, J.L. Durán, L.M. Bradshaw, A.M. Farag, Ammonia and aquatic ecosystems: A review of global sources, biogeochemical cycling, and effects on fish, Sci. Total Environ. 907 (2024) 167911. https://doi.org/10.1016/j.scitotenv.2023.167911.

DOI: https://doi.org/10.1016/j.scitotenv.2023.167911

[12]   W. Feng, T. Wang, Y. Zhu, F. Sun, J.P. Giesy, F. Wu, Chemical composition, sources, and ecological effect of organic phosphorus in water ecosystems: A review, Carbon Res. 2 (2023) 12. https://doi.org/10.1007/s44246-023-00038-4.

[13]   Ministry of Health of the Republic of Indonesia, Regulation of the Minister of Health of the Republic of Indonesia Number 2 of 2023 concerning the Implementation of Government Regulation Number 66 of 2014 on Environmental Health, Jakarta, Indonesia, 2023.

[14]   A. Khoeriyah, Anies, Bacteriological quality aspects of refill drinking water depots (DAMIU) in West Bandung Regency, Maj. Kedokt. Bandung 47 (2015) 137–144. https://doi.org/10.15395/mkb.v47n3.594.

DOI: https://doi.org/10.15395/mkb.v47n3.594

[15] Y. Kristianingsih, M. Masdianto, A. Mardikawati, Determination of iron (Fe) and manganese (Mn) concentrations in groundwater around Setu Pedongkelan, Depok, Anakes J. Ilm. Analis Kesehat. 7 (2021) 148–156. https://doi.org/10.37012/anakes.v7i2.686.

DOI: https://doi.org/10.37012/anakes.v7i2.686

[16]   National Standardization Agency of Indonesia (BSN), SNI 6989.57:2008. Water and Wastewater—Part 57: Surface Water Sampling Method, Jakarta, 2008.

[17]   National Standardization Agency of Indonesia (BSN), SNI 6989.4:2009. Water and Wastewater—Part 4: Determination of Iron (Fe) by Flame Atomic Absorption Spectrophotometry, Jakarta, 2009.

[18]   National Standardization Agency of Indonesia (BSN), SNI 6989.5:2009. Water and Wastewater—Part 5: Determination of Manganese (Mn) by Flame Atomic Absorption Spectrophotometry, Jakarta, 2009.

[19]   National Standardization Agency of Indonesia (BSN), SNI 06-6989.30-2005. Water and Wastewater—Part 30: Determination of Ammonia by the Phenate Spectrophotometric Method, Jakarta, 2005.

[20]   National Standardization Agency of Indonesia (BSN), SNI 6989-31:2021. Water and Wastewater—Part 31: Determination of Orthophosphate and Total Phosphorus by Ascorbic Acid Reduction Spectrophotometry, Jakarta, 2021.

[21]   H. Tong, Z. Li, X. Hu, W. Xu, Z. Li, Metals in occluded water: A new perspective for pollution in drinking water distribution systems, Int. J. Environ. Res. Public Health 16 (2019) 2849. https://doi.org/10.3390/ijerph16162849.

DOI: https://doi.org/10.3390/ijerph16162849

[22]   S.S. Kullar, et al., A benchmark concentration analysis for manganese in drinking water and IQ deficits in children, Environ. Int. 130 (2019) 104889. https://doi.org/10.1016/j.envint.2019.05.083.

DOI: https://doi.org/10.1016/j.envint.2019.05.083

[23]   P.B. McMahon, K. Belitz, J.E. Reddy, T.D. Johnson, Elevated manganese concentrations in United States groundwater: Role of land surface–soil–aquifer connections, Environ. Sci. Technol. 53 (2019) 29–38. https://doi.org/10.1021/acs.est.8b04055.

DOI: https://doi.org/10.1021/acs.est.8b04055

[24]      M. Ramachandran, K.A. Schwabe, S.C. Ying, Shallow groundwater manganese merits deeper consideration, Environ. Sci. Technol. 55 (2021) 3465–3466. https://doi.org/10.1021/acs.est.0c08065.

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Published

2026-07-08

How to Cite

Megantari, V., Amilia, N., Rosita, N., Permata, W., & Hatiningsih, F. (2026). Physicochemical Characterization and Water Quality Feasibility across Three Source Water Types in the Ciputat Area, South Tangerang. Journal of Biotropical Research and Nature Technology, 5(1), 75–86. https://doi.org/10.47352/jbrnt.2964-0431.456