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Hydrobiogeochemical evolution along the regional groundwater flow systems in volcanic aquifers in Kumamoto, Japan

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Kumamoto is known as the largest groundwater city in Japan. Geochemical modeling (saturation indices and mineral stability diagram) was applied in this area for better understanding a hydrogeochemical evolution in volcanic aquifers in regional scale with additional constraint from stable isotopic dataset. Geochemical evolutionary model was interpreted along the water flow dynamics. In total 136 water samples were collected from wells, springs, and rivers in and around the major groundwater flow lines for geochemical analyses. Our results indicated that plagioclase is the major weathering reactant in aquifers with secondary important weathering minerals of pyroxenes. These reactions facilitate current hydrochemical signatures and produce secondary minerals of kaolinite or halloysite and smectite in later stage. Observed hydrogeochemical processes can be distinguished into two distinct criteria along flow regime. The first processes are material loads from the surface (mixing of contaminants and river waters) and initial stage of silicate weathering, resulting in the formation of Ca-HCO3, Ca-NO3–HCO3, and Ca–Mg–Na-HCO3 type waters. These processes prevail in aquifers at the recharge to lateral flow zones with relatively shorter residence time of < ca. 40 years. The second processes are the precipitation of clay minerals, i.e., smectite, and cation exchange reaction of Ca²⁺ and Mg²⁺ to Na⁺ in downslope aquifers (Na-HCO3 type) with relatively longer groundwater residence time of > 55 years. Microbiological reduction reactions dominate over these areas and salinization occurs at the coast that changes aquifer waters to be Na-Cl type. Proposed models and approach shown in this study may be useful and applicable in interpreting systems in other volcanic aquifer systems at similar climate conditions and for sustainable water resources management.
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Environmental Earth Sciences (2020) 79:410
https://doi.org/10.1007/s12665-020-09155-4
ORIGINAL ARTICLE
Hydrobiogeochemical evolution alongtheregional groundwater ow
systems involcanic aquifers inKumamoto, Japan
TakahiroHosono1,2 · ShahadatHossain3· JunShimada1
Received: 18 September 2019 / Accepted: 27 August 2020 / Published online: 7 September 2020
© Springer-Verlag GmbH Germany, part of Springer Nature 2020
Abstract
Kumamoto is known as the largest groundwater city in Japan. Geochemical modeling (saturation indices and mineral stabil-
ity diagram) was applied in this area for better understanding a hydrogeochemical evolution in volcanic aquifers in regional
scale with additional constraint from stable isotopic dataset. Geochemical evolutionary model was interpreted along the
water flow dynamics. In total 136 water samples were collected from wells, springs, and rivers in and around the major
groundwater flow lines for geochemical analyses. Our results indicated that plagioclase is the major weathering reactant
in aquifers with secondary important weathering minerals of pyroxenes. These reactions facilitate current hydrochemical
signatures and produce secondary minerals of kaolinite or halloysite and smectite in later stage. Observed hydrogeochemical
processes can be distinguished into two distinct criteria along flow regime. The first processes are material loads from the
surface (mixing of contaminants and river waters) and initial stage of silicate weathering, resulting in the formation of Ca-
HCO3, Ca-NO3–HCO3, and Ca–Mg–Na-HCO3 type waters. These processes prevail in aquifers at the recharge to lateral flow
zones with relatively shorter residence time of < ca. 40years. The second processes are the precipitation of clay minerals,
i.e., smectite, and cation exchange reaction of Ca2+ and Mg2+ to Na+ in downslope aquifers (Na-HCO3 type) with relatively
longer groundwater residence time of > 55years. Microbiological reduction reactions dominate over these areas and salini-
zation occurs at the coast that changes aquifer waters to be Na-Cl type. Proposed models and approach shown in this study
may be useful and applicable in interpreting systems in other volcanic aquifer systems at similar climate conditions and for
sustainable water resources management.
Keywords Groundwater· Volcanic aquifer· Saturation indices· Silicate weathering· Cation exchange· Flow dynamics
Introduction
Kumamoto is the largest groundwater user area in Japan
(Fig.1). About one million people in and around the area
completely depend on groundwater for their all purposes
(e.g., Taniguchi etal. 2019). The area comprises Kumamoto
City and its surrounding districts and towns, extended to the
western flank of Aso caldera mountains in central Kyushu
(Fig.1), which is one of the largest volcanic calderas in
Japan. The abundant groundwater resources in this area
are a blessing of combination of both high local precipi-
tations and highly permeable surface geological structures
that comprise of Quaternary pyroclastic flow deposits of
the Aso volcanic eruptions. Since the people in Kumamoto
relies on groundwater for drinking purpose, its quality is one
of major concerns to the local citizens and policy makers
in a management point of view. However, the groundwater
quality is becoming a serious issue in this area due to some
Electronic supplementary material The online version of this
article (https ://doi.org/10.1007/s1266 5-020-09155 -4) contains
supplementary material, which is available to authorized users.
* Takahiro Hosono
hosono@kumamoto-u.ac.jp
1 Faculty ofAdvanced Science andTechnology, Kumamoto
University, 2-39-1 Kurokami, Kumamoto860-8555, Japan
2 International Research Organization forAdvanced Science
andTechnology, Kumamoto University, 2-39-1 Kurokami,
Kumamoto860-8555, Japan
3 Atomic Energy Centre, Chittagong, Bangladesh Atomic
Energy Commission, 1018/A, Bayezid Bostami Road, East
Nasirabad, Chittagong4209, Bangladesh
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
... Groundwater flow systems and basic water quality in Kumamoto are well acknowledged through traditional borehole measurements (water table, temperature, and water quality measurements) using many wells installed over the entire area (Fig. 1a and b;Nagai et al., 1983, Kumamoto Prefecture andKumamoto City, 1995;Taniguchi et al., 2003). More detailed aquifer environmental conditions were revealed in recent years from multidisciplinary approaches including groundwater age determination (Kagabu et al., 2017, geochemical modeling (Hossain et al. 2016a;Hossain et al., 2016b;Hosono et al., 2020a), multiple stable isotope (Hosono et al., , 2020b. (b) The locations of the wells for groundwater sampling by this study. ...
... The thickness of the aquifers is about ~ 250 m, which tends to be thicker toward the coastline, and groundwater flows along the topographical gradient from north or east to west (Fig. 1a). The aquifers are divided into an upper unconfined shallow aquifer (layer thickness ~ 90 m, which we call the 1st aquifer) and a lower confined to semiconfined deep aquifer (layer thickness 20 ~ 250 m, which we call the 2nd aquifer) across the impermeable layer of the lacustrine sediments (Hosono et al., 2020a;Hosono et al., 2020b). Groundwater is recharged from the surrounding mountains, the plateaus (50 to 200 m above sea level), and the river water in the midsection of the Shira River, and flows laterally to the plains (Fig. 1a). ...
... Most of the groundwater discharge near Ezu Lake, at the locations where the topographical gradient becomes gentle, but a part of it still stays under the ground and exists as a relatively slow-flowing groundwater toward the coast (Fig. 1a). See previous studies (Hosono et al., 2013, Hosono et al. 2014, Hosono et al., 2020aHosono et al., 2020b, Rahman et al., 2021 for a more detailed description of regional aquifer conditions. ...
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... In many regions of the world, volcanic aquifers have become valuable resources in providing water for human consumption and economic activities (Bertrand et al. 2010;El Maghraby 2015;Hosono et al. 2020;Koh et al. 2018;Morán-Ramírez et al. 2016). Approximately 65% of the population in the Central Valley (Valle Central), Costa Rica, equivalent to 1.7 million people, depends on groundwater resources from the Barva-Colima volcanic aquifer system (Reynolds- Vargas et al. 2006). ...
... DA has been successfully applied in volcanic systems, combined with other multivariate methods (Barzegar et al. 2019;Panagopoulos et al. 2016) and machine learning procedures (Ha et al. 2021;Sajedi-Hosseini et al. 2018). Moreover, principal component analyses (PCA; Gan et al. 2018;Panagopoulos et al. 2016;Pazand and Javanshir 2016), correlation analyses (Morán- Ramírez et al. 2016;Kim et al. 2020), factor analysis (Gan et al. 2018); hierarchical cluster analysis Egbueri 2020;Gan et al. 2018); hydrochemical diagrams (Ebrahimi et al. 2022;Fenta et al. 2020;Hosono et al. 2020;Shishaye et al. 2020;Wisitthammasri et al. 2020), base exchange indices (Haji et al. 2021;Mechal et al. 2017), multiple linear regression , and the assessment of saturation indexes of aqueous mineral phases (Esteller et al. 2017;Hosono et al. 2020;Morán-Ramírez et al. 2016) are widely employed to facilitate the interpretation of geochemical processes with large hydrochemical data series in volcanic aquifers. ...
... DA has been successfully applied in volcanic systems, combined with other multivariate methods (Barzegar et al. 2019;Panagopoulos et al. 2016) and machine learning procedures (Ha et al. 2021;Sajedi-Hosseini et al. 2018). Moreover, principal component analyses (PCA; Gan et al. 2018;Panagopoulos et al. 2016;Pazand and Javanshir 2016), correlation analyses (Morán- Ramírez et al. 2016;Kim et al. 2020), factor analysis (Gan et al. 2018); hierarchical cluster analysis Egbueri 2020;Gan et al. 2018); hydrochemical diagrams (Ebrahimi et al. 2022;Fenta et al. 2020;Hosono et al. 2020;Shishaye et al. 2020;Wisitthammasri et al. 2020), base exchange indices (Haji et al. 2021;Mechal et al. 2017), multiple linear regression , and the assessment of saturation indexes of aqueous mineral phases (Esteller et al. 2017;Hosono et al. 2020;Morán-Ramírez et al. 2016) are widely employed to facilitate the interpretation of geochemical processes with large hydrochemical data series in volcanic aquifers. ...
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... The unconfined aquifer is composed of recent pyroclastic-flow deposits (uppermost Aso-4) and partial marine sediments (<50 m deep). The underlying confined/semi-confined aquifer consists of older pyroclastic deposits and volcanic flow lavas (60-250 m) [45,54]. ...
... The Kumamoto area lies in central Kyushu Island, southwestern Japan ( Figure 1). Hossain et al. [43,44] and Hosono et al. [45] reported its geological and hydrogeological settings and the geochemical processes controlling its groundwater. The eastern part of the study area is a volcanic area of the Quaternary age covered by pyroclastic-flow deposits erupted from the Aso volcano and alluvial deposits of the Pleistocene age. ...
... The eastern part of the study area is a volcanic area of the Quaternary age covered by pyroclastic-flow deposits erupted from the Aso volcano and alluvial deposits of the Pleistocene age. The western portion (especially coastal area) comprises the Kumamoto alluvial plain, consisting of Holocene Ariake clay [45,46]. The pyroclastic-flow deposits erupted from Mt. Aso over four periods between 90 and 30 ka and are classified into four types: Aso-4, Aso-3, Aso-2, and Aso-1. ...
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... The main challenge for developing such a model is the collection of long-term tracer measurement data over a regional scale. The model domain of this study addresses regional groundwater flow systems in Kumamoto in the central part of Kyushu Island in southern Japan (Fig. 1); several studies (Taniguchi et al. 2003;Hosono et al. 2013Hosono et al. , 2014Hosono et al. , 2020Hossain et al. 2016a, b;Zeng et al. 2016;Kagabu et al. 2017;Okumura et al. 2018) have characterized the groundwater age, flow dynamics, and biogeochemical processes using several tracers such as groundwater age tracers including sulfur hexafluoride (SF 6 ), tritium ( 3 H), chlorofluorocarbons (CFCs) and krypton ( 85 Kr), stable isotope ratios of water molecular (δD and δ 18 O), and aquifer temperature profiles. These studies demonstrated that the groundwater age tracers such as 3 H and 85 Kr concentrations are the most useful variables, while SF 6 and CFCs cannot be used for proper age determination due to contamination effects (Kagabu et al. 2017;Ide et al. 2020). ...
... The aquifers in the study area are separated by the Futa and Hanafusa impermeable sediment layers into unconfined (named as the first aquifer) and semiconfined to confined aquifers (named as the second aquifer; Fig. S1 of the ESM; Taniguchi et al. 2003;Hosono et al. 2013Hosono et al. , 2019Hosono et al. , 2020Rahman et al. 2020b). The first aquifer consists of unwelded Aso-4 pyroclastic deposits and alluvium sedimentary deposits, and the depth of this aquifer varies between a few meters to 90 m. ...
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... Understanding the material cycle in the ecosystem and biogeochemical processes is essential for comprehending changes in the physical and chemical properties of water within a basin. These processes also apply to groundwater and surface water Hosono et al. 2020). Water quality, watershed management, and systemic hydrological environmental factors are all crucial (Wu and Lu 2021;Xu et al. 2022a;Zhao et al. 2022). ...
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... G2, G3, G4, and most of G1 are saturated with quartz and kaolinite (Table 5). Following Hosono et al. [72], incongruent dissolution reactions of silicate weathering in the study area can be hypothesized by following Equations (9) and (10) ...
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Study region: The Kumamoto area (945 km2) in the south of Japan, where almost 100% of the drinking water is dependent on groundwater. Study focus: Simultaneous measurement of groundwater dating tracers (85Kr, chlorofluorocarbons [CFCs], sulphur hexafluoride [SF6], and 3H) was performed in the Kumamoto area, to elucidate the regional groundwater flow system and obtain improved estimates of groundwater ages. The groundwater ages were estimated from the 85Kr concentrations in nine locations from three areas: along two major groundwater flow lines (A–A’ and B–B’); and a high-nitrate-input recharge area (C area). New hydrological insights for the region: The groundwater ages could not be estimated using CFCs or SF6, particularly in the urban areas because of artificial additions to the concentration over almost the entire study area. However, even in these regional circumstances, apparent ages of approximately 16, 36, and not less than 55 years were obtained for three locations on the A–A’ line (recharge area, discharge area, and stagnant zone of groundwater, respectively) from 85Kr measurements. This trend was also supported by lumped parameter model analysis using a time series of 3H observations. In contrast, along the B–B’ line, the groundwater age of not less than 55 years at three locations, including the recharge to discharge area, where CFCs and SF6 were not detected, implies old groundwater: this is also the area in which denitrification occurs. In the C area, very young groundwater was obtained from shallow water and older groundwater was detected at greater depths, as supported by the long-term fluctuations of the NO3−–N concentration in the groundwater. The results of this study can be effectively used as a “time axis” for sustainable groundwater use and protection of groundwater quality in the study area, where groundwater accounts for almost 100% of the drinking water resources.
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There are growing concerns about nitrate contamination in Kumamoto City, where >700,000 people completely depend on groundwater as a source of drinking water. We found that some groundwater samples showed considerably different nitrate concentrations although their sampling locations were close to one another, and we speculated that this phenomenon was due to the differences in subsurface geological properties. In order to verify this hypothesis, we carried out temporally intensive long-term monitoring of the groundwater levels and water qualities at three of the closely related sampling wells, and the results revealed that the changes in water level and water quality were different at each well. The water level at well T1, where nitrate concentrations ranged from 12 to 26 mg N/L, showed a significantly sensitive and unique response to heavy rain, which indicated that the subsurface at this site might be highly permeable; this would have allowed for the influent water to easily reach the groundwater aquifer over a short period. However, wells T2 and T3, which were located within 0.6 and 1.9 km from well T1, respectively, had nitrate concentrations that were lower than that in well T1 (4.5–8.0 mg N/L) and showed only gradual responses to heavy rain. These observations suggest that the highly permeable subsurface properties in the vicinity of well T1 contributed to the more serious nitrate contamination in well T1 than those at wells T2 and T3. This study demonstrates the importance of temporally intensive, long-term monitoring for capturing changes in groundwater level and water quality with precipitation fluctuations, and we showed how this approach can lead to a better understanding of the nitrate contamination situation.
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