Over 40 million people live on and exploit the groundwater resources of the Kanto Plain. The Plain encompasses metropolitan Tokyo and much of Chiba Prefecture. Useable groundwater extends to the base of the Kanto Plain, some 2500 to 3000 m below sea level. Much of the Kanto Plain surface is at sea level. By the early 1970s, with increasing urbanization and industrial expansion, local overdraft of groundwater resources caused major ground subsidence and damage to commercial and residential structures as well as to local and regional infrastructure. Parts of the lowlands around Tokyo subsided to 4.0 m below sea level; particularly affected were the suburbs of Funabashi and Gyotoku in western Chiba. In the southern Kanto Plain, regulations, mainly by local government and later by regional agencies, led to installation of about 500 monitoring wells and almost 5000 bench marks by the 1990's. Many of them are still working with new monitoring system. Long-term monitoring is important. The monitoring systems are costly, but the resulting data provide continuous measurement of the “health” of the Kanto Groundwater Basin, and thus permit sustainable use of the groundwater resource.
The Kanto plain is also called “the Kanto fore-arc submarine basin” or “the paleo-Kanto-submarine basin”, based on surrounding geologic and physiographic features such as Nasu Volcanic Zone, Fuji Volcanic Zone, Japan trench and Izu-Ogasawara Trench (Nirei et al., 1990). Over 40 million people live on the Kanto plain which includes the Tokyo metropolis. The waterfront area around Tokyo Bay mostly includes both alluvium and man-made strata such as reclaimed areas and is densely covered with houses and factories. Sediments of the Kanto basin are 2500–3000 m thick and are of Miocene to Holocene age. The basin is also called the Kanto groundwater basin from the standpoint of the production of groundwater, natural gas and iodine which are contained in fossil sea water. Uncontrolled use of groundwater has caused land subsidence. To ensure effective use of groundwater, a monitoring system for their management has been developed. The system has about 500 self-recording observation wells, almost 5000 bench marks (leveled every year). Over-pumping of the groundwater (fresh water and brine groundwater) resulted in a serious land subsidence problem in various areas, especially alluvial plains and reclaimed area so that it was inevitable to control the groundwater use to solve the problem (Aihara et al., 1969). Consequently, systematic observations of pumping up volumes, groundwater level changes and land subsidence records for the effective groundwater use have been carried out for preventing the land subsidence from a geological point of view (Research Committee on Land subsidence Prevention in Southern Kanto District, 1974).
The Kanto Paleo-submarine basin can be called the Kanto groundwater basin from the standpoint of the distribution and the fluidity of the underground fluid resources (Nirei and Furuno, 1986). The bottom of the groundwater basin corresponds to the base of Kanto tectonic basin, which is situated at 3000–2500 m below the surface. The sediments of the Kazusa sub-groundwater basin in the basin contains brine groundwater (fossil sea water) including natural gas and iodine (Figs. 1, 2). The equivalent layer of the Kazusa Group that extended to the western and northern part of the Kanto plain is composed of alternating beds of coarse- to fine-grained deposits is suitable for groundwater. The lower part of the Shimosa sub-groundwater basin contains groundwater colored with humid material from the northern to central part of the Boso peninsula, and the colored groundwater is unsuitable for drinking. In the upper part of the Shimosa sub-groundwater basin, most of the aquifer layers contain fresh water; this basin had the largest pumpage volume of water in the Kanto groundwater basin. However, the more pumping up volume increased, the lower the groundwater level became in the Shimosa upper sub-groundwater basin. Which is also resulted in lowering of groundwater level even in the alluvial deposits as well as subsiding of ground surface. It is now widely confirmed that the amount of ground subsidence is affected by the thickness of alluvial deposits (Research Institute of Environmental Geology, 1979).
Schematic section of the Kanto groundwater basin: 1: alluvial deposits, 2: upper part of the Shimosa Group, 3: lower part of the Shimosa Group, 4: Kazusa Group, 5: Miura Group.
Kanto groundwater basin and the distribution of monitoring wells and benchmarks. Large dots: monitoring wells, small dots: benchmarks. A–E: monitoring wells which data were used in Fig. 3.
Natural gas and groundwater have been produced as the underground fluid
resources in the Kanto groundwater basin. The former is mainly derived from
the Kazusa sub-groundwater basin. Annual production of natural gas was
520
Groundwater and brine groundwater were pumped up disorderly by companies, farmers and local governments for industry, agriculture, drinking water supply and production of natural gas and iodine before 1960s. However, the regulation by national government began in the middle 1960s and local governments began from the 1970s as progress of the subsidence became remarkable in order to prevent land subsidence.
Each local government has attempted to regulate the pumping volume of the
groundwater in order to prevent land subsidence from 1970s. For example,
users are required to report the pumping volume compulsorily. Criteria of
depth and diameter of discharge pipes were set up (Prefectural Governors'
Committee for Land subsidence Prevention in Kanto District, 1983). An
agreement to control the pumping of fossil sea water containing natural gas
was also made between the Chiba prefecture administration and each gas
production company. The condition of groundwater levels in the whole Kanto
groundwater basin has recently been clarified. The number of observation
wells was 375 in total as of 1982 (Furuno et al., 1983), 459 as of 1991 and
about 500 as of 2010s. The amount of land subsidence has been measured by
yearly precise leveling. The number of benchmarks attained 4880 and the total
length of the leveling, 7363.6
Historical change of the groundwater level in the Kanto groundwater basin. A: Ken-15 (Tokyo), B: Kannongawa (Kawasaki), C: W-2 (Chiba), D: W-25 (Chiba), E: Kawaguchi-1 (Saitama), F: Kuki (Saitama), G: Sowachu (Ibaraki), H: Oyama1–2 (Tochigi).
In the Keihin industrial zone (coastal zone of Tokyo, Yokohama and Kawasaki) located in the south western part of the Kanto groundwater basin, the land subsidence caused by over-pumping of groundwater were recognized in early 1940s. As a result, industrial aqueducts were established to replace the groundwater pumping from the coastal zone of Kawasaki and Yokohama. In the industrial zone, the pumping was controlled in the 1950s by regulations on the depth of wells and the diameter of discharge pipes. In the industrial zone of Tokyo and its suburbs, the pumping volume was controlled in the 1960s by two laws concerning industrial water and pumping at building sites. However, the countermeasures for land subsidence were often loosely applied by groundwater users, especially the industrial users. In the 1970s, with the rapid growth of the Japanese economy, land subsidence have been recognized as the most important problems. In such a social background, not only the national government enacted the strict criteria for the regulation concerning the industrial water and the pumping up law for building use, but also the prefectural governments in the southern part of the Kanto groundwater basin strictly applied these regulations. As a result, the groundwater level and the land subsidence stopped gradually. It was even recognized in certain regions that the groundwater level rose. However, excessive regulations produce another problem in some areas. Tokyo Station and Ueno Station in Tokyo set up deep underground platforms before early 1960s when groundwater level was low. Groundwater level rose from late 1960s and buoyancy acted on the building. Those stations had to set up anchors and weights as a countermeasure of buildings rising by buoyancy. Rising of groundwater level in man-made strata and Holocene deposit increase the risk of liquefaction-fluidization. We need to keep proper groundwater level.
It was in the early 1960s that the groundwater level fell to 60 m below sea
level in the coastal industrial zone of Tokyo metropolis. After that, the
recovery of the groundwater level was monitored according to the pumping up
control. In the 1970s the regulations were strictly adhered to in the
southern Kanto groundwater basin. Accordingly, in the years from 1975 to
1980, the groundwater level recovered 30–40
The land surface has been sinking to below sea level in the downtown Tokyo area for mixed industry and residential uses (Shitamachi) since 1910s. Coincidentally, the areas showing ground level lower than mean sea level and high water level of ordinary spring tide of Tokyo Bay were widely scattered. Recently, however, these phenomena have been recognized in alluvial area not only in Shitamachi of Tokyo, but also in suburbs of Tokyo such as Kawasaki and Yokohama in Kanagawa Prefecture, Funabashi, Gyotoku and Urayasu on western Chiba Prefecture. This land subsidence has been stabilized by the regulation of the pumping. The land subsidence was stopped in certain areas and the ground surface slightly uplifted by the recovery of the groundwater level. On the other hand, in the area from central to northern part of the Kanto groundwater basin, land subsidence has begun to sink as a result of over-pumping. That is, land subsidence area is moving northward. Land subsidence before 1970s spread lowland area around Tokyo Bay and Kujyukuri in Boso Peninsula which faced the Pacific Ocean (Fig. 5).
Confined groundwater level in the Kanto groundwater basin (especially the Shiosa sub-groundwater basin). Lowest contour line shows 10 m below sea level.
Lowland area around Tokyo Bay and Kujyukuri which faced the Pacific Ocean.
It is necessary to establish a more effective monitoring system for continuous observation of the groundwater pumping, groundwater level and land subsidence, and to decide the pumping volume in consideration of the change of the groundwater level and the ground movement with the law of dynamic equilibrium between man and nature due to the relation among human groups. In other words, the groundwater resources can be used while the health condition of the groundwater basin is examined by periodical health checks. The long-term monitoring of land subsidence and groundwater is important for the sustainable use of the groundwater in the groundwater basin.
We sincerely appreciate members of Research Institute of Environmental Geology, Chiba and members of the local governments of Kanto district who have developed a monitoring system and kept on recording land subsidence and groundwater level.