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WO2002099202A1 - Hydroelectric power generating method - Google Patents

Hydroelectric power generating method Download PDF

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Publication number
WO2002099202A1
WO2002099202A1 PCT/JP2002/005476 JP0205476W WO02099202A1 WO 2002099202 A1 WO2002099202 A1 WO 2002099202A1 JP 0205476 W JP0205476 W JP 0205476W WO 02099202 A1 WO02099202 A1 WO 02099202A1
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WO
WIPO (PCT)
Prior art keywords
water
dam
pipe
power generation
gravel
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
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PCT/JP2002/005476
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French (fr)
Japanese (ja)
Inventor
Norio Takei
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NAGAI KOSHO CO Ltd
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NAGAI KOSHO CO Ltd
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Priority to JP2003502299A priority Critical patent/JPWO2002099202A1/en
Publication of WO2002099202A1 publication Critical patent/WO2002099202A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B9/00Water-power plants; Layout, construction or equipment, methods of, or apparatus for, making same
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/60Ecological corridors or buffer zones
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E10/00Energy generation through renewable energy sources
    • Y02E10/20Hydro energy

Definitions

  • the present invention relates to a natural environment-friendly, safe, and economically advantageous hydroelectric power generation method that can permanently maintain hydroelectric power, pumped-storage power generation, flood protection, water use, sabo control, fishway security, and the like.
  • Dams also block the flow of organic matter, break the food chain and destroy ecosystems. That is, eutrophication of dam lakes, frequent occurrence of plant blank tons, emission of odors such as mold odor, generation of carcinogenic substance trihalomethane, and deterioration of tap water quality. It also undermines the lower reaches of the dam, drastically reduces plankton, sharply reduces the amount of seafood that feeds on it, and reduces coastal fishing.
  • boulders of various sizes are scattered and buried in the riverbed. If boulders are sucked, the flow velocity in the water pipe will be significantly reduced and clogging may occur in the intake pipe, water pipe, and sand discharge pipe.
  • boulders may flow from the ground to the dam lake, and the boulders may bury the water pipe or be sucked into the water pipe.
  • dams are multipurpose dams, but very few dams fully fulfill multipurpose functions. There are only a few dams that can store all the floods from the upper reaches, and most of them are limited water level or pre-discharge type.
  • the restricted water level method is to release water during the period when floods are expected to occur, lower the storage level to a certain level, and secure sufficient capacity to control floods. It is a method. This release is an ineffective release and has a negative effect from both sides of hydropower generation and water use.
  • preliminary discharge is a method in which when water is expected to flow out, the water is released in a short time to lower the water level. This release is also an invalid release, which has a negative effect on both hydropower and water use.
  • a large amount of wastewater is released by the peak cut method, and there is a problem that the flow rate does not decrease when it is desired to reduce the flow rate in the downstream. Unless it is a very large flood control dam, it is not possible to have a full-fledged control system that stores the entire amount of flood water.
  • the concentration of methane at the mouth of the carcinogen triha in tap water is on the rise and is a problem. It is caused by the metabolism of algae in raw tap water.
  • Organic substances such as decomposition products are the causative substances, and are produced in response to chlorine added at water treatment plants.
  • the causative substances such as metabolites and decomposed substances having trihalomethane-producing ability are not decomposed in a short period of time and accumulate.
  • dam lakes which have a large storage capacity compared to the inflow water, are likely to increase the trihalomethane production capacity of the lake water by accumulating decomposition products of algae.
  • Factors that determine the trihalomethane production capacity of dam lake water are the degree of algae growth and water turnover.
  • the lake water flows and the surface layer To make good contact with the soil. It is considered that the soil has the ability to remove humic substances in the water because the groundwater does not contain trihalomethane-causing substances.
  • the dam lake is buried in a short period of time due to the flowing sediment, so the amount of water that can be generated is only the amount of water during the ⁇ flood season, and the amount of water during the flood season and during the flood is invalidated. This is a factor that increases power generation costs.
  • the present invention has been made to solve the above-mentioned problems of the power generation system using a conventional dam including such a small-scale dam, and the object thereof is to use a large amount of energy without using a huge amount of energy.
  • Sand while hydropower The gravel can be transported to the plain and the permanent functions of the dam, such as hydroelectric power, pumped-storage power, flood protection, water use, sabo, and fishway access, can be maintained forever. To propose a new hydropower method.
  • the present invention provides an intake pipe extending upstream from the dam dam at the bottom of the dam lake, an intake port at the tip thereof, and a plurality of branch pipes along the bottom of the dam lake in the middle of the intake pipe.
  • a water intake is provided at the tip of the water intake, and a water intake pipe is connected to the water intake pipe through a drain valve, and is provided downstream of the dam dam and connected to a turbine of the power plant.
  • there is a hydroelectric power generation method in which water is supplied from a water pipe to a turbine of a power plant to generate electricity, and sediment and organic substances flowing down to a dam lake are sucked and discharged from intakes of water pipes and branch pipes.
  • the water intake pipe is composed of a plurality of pipes connected via flexible pipe joints, and the water intake at the tip of each pipe can be moved to every corner of the lake bottom, and the inner surface of each pipe is formed. Lining with a lining tube with a colored urethane rubber layer provided on the outer peripheral surface of a soft rubber tube. When the soft rubber wears and the urethane rubber layer is exposed, prepare the lining replacement and replace only the lining.
  • This is a hydroelectric power generation method characterized by making the service life of an intake pipe permanent.
  • Fig. 1 the sediment sucked into the intake pipe 1c is allowed to merge with the large-diameter water pipe 1a (usually 3m) through the drain valve 21 and is connected to many other dams and water pipes. The water will be led to the power plant by joint use.
  • the conventional small-scale dam can use only 1/3 of the total water volume during the ⁇ flood season.
  • the head becomes several times (m times) and the flow rate becomes 3 Therefore, the power generation will be 3 xm times and the power generation efficiency QH / V (H: head) can be maximized.
  • a float tank 23 to the water intake 22 a and the branch 22 b of the water intake pipe to suck and discharge all the soil and organic matter from the dam lake to every corner. Compressed air is sent to the inside to float, and compressed air is injected, changing its position and submerging it at the sediment accumulation position. These operations are performed by computer control and remote operation. To facilitate this movement, the intake pipe 1c and the branch pipes are connected by flexible steel pipe joints as described later.
  • boulders buried in the riverbed 4 and the bottom of the dam lake were dug up before the construction of the dam, and crushed with a crusher to the size of gravel (up to 60 mm). It is desirable to be easily sucked into the intake pipe or fixed with cement.
  • V c 4.0 .0 (d) 1/2
  • V c is 1.0 ms.
  • the flow velocity decreases in inverse proportion to the cube of the distance, but for gravel with a diameter of 60 mm or less, even if it is some distance from the intake 22 Suction is possible, and there is no risk of clogging in the water pipe 1, and it can flow down with a small flow resistance and can be transported to the gravel accumulation site.
  • gravel When such gravel is sent to the gravel accumulation site, it can be used for concrete aggregate only by sieving.
  • a fish pool is set up on the downstream side of the dam dam, and a submerged fishway is established from the fish pool to the dam lake.
  • the reservoir of the dam lake is opened through the diverter valve and drained into the water pipe, and the water level that goes up to the fish collection pool is lost.
  • the fish that have gone upstream to the fish collection pool (secondary dam) 25c downstream of the dam embankment pass through the cave fishway 26c to the dam lake. .
  • the predetermined water level H 2 is the water level difference ⁇ h at which the migratory fish coming upstream from the fish collection pool (secondary dam) installed downstream of the dam dam can travel upstream through the submerged fishway. It is usually 0.2 m.
  • the maximum velocity V o in the cave fishway at that time can be obtained by the following equation, where g is the acceleration of gravity and ⁇ h is the head.
  • V o (2 g-A h) 1/2
  • the head of A h is the difference between the water level of the dam and the water level of the fish collection pool. Therefore, H2 is the water level higher than the water level of the fish collection pool (secondary dam) by ⁇ h calculated by the above equation. If h is 0.2 m and the sluice of the cave fishway is opened, the maximum velocity V o in the cave fishway will be 2 m / sec. When a migratory fish goes up the fishway, it goes up at the lunge speed of the fish. Its rush speed is (10 times the length of the fish) / sec. However, the charge speed is 6 seconds Or can't last. The long-lasting cruising speed is 2 to 4 times the length of the fish per second.
  • the flow velocity in the fishway must be lower than the fish rush speed.
  • the sluice gate of the cave fish passage 26c is opened, the fish of the fish catching bull 25c feels the flow in the body and stimulates the instinct to instinct, swims against the current and swims through the fishway to the upper dam lake. Up.
  • a boulder flow prevention dam is created upstream of the dam lake, and the dam flows gravel and water with a particle size of less than a predetermined value into the dam lake, and boulders with a particle size exceeding a predetermined value Driftwood and tree branches have vertical cuts (gap) so that they can be closed there.
  • a fish collection pool is installed upstream of the boulder flow prevention weir, and a dam lake is also installed downstream. There will be other fish collection pools that communicate with each other, and a plurality of submarine fishways and their locks will be provided between the upstream fish collection pool and the boulder flow prevention dam and between the dam lake and the other fish collection bulls, respectively. It is desirable to open and close the sluice in a timely manner so that fish can move in both directions, upstream and downstream.
  • boulders are periodically ground with a crusher to a particle size of less than a predetermined value and flow down to the dam lake, or fixed with cement so that they do not flow into the dam lake. It can be effectively prevented from flowing into the lake.
  • a dam 24 is installed upstream of the dam lake to prevent boulder flow, and a vertical cut is formed in the dam to reduce the particle size below the gravel (60 mm or less). Only the sand and gravel will flow down through the cut I'm sorry.
  • boulders blocked by the above dam 2.4 are periodically crushed to the size of gravel by a crusher and flow down to the dam lake through submerged fish passages 26a and 26b installed in the dam. Let it do.
  • embankment 24 will create an arc-shaped embankment projecting downstream, so that the boulders flowing down gather in the center of the arc.
  • the diving fishway gate 26b are installed at multiple locations.
  • the fish collection pool should be constructed so that it always has sufficient depth for fish to live.
  • the fishing pool will be filled with boulders and sediment, and some of the pits will not function, but the pits at both ends of the dam will be able to function.
  • the boulders that fill the fish collection pool are periodically crushed to the size of gravel using a crusher, and then flow to Dam Lake via the pit cave 26a, the fish pool 25b, and the pit cave 26b.
  • the hydroelectric power generation of the present invention is a method in which a dam is built stepwise from the uppermost stream of a river, and the dam penetrates into the underground aquifer many times more than the conventional one.
  • the water in this aquifer returns to the river again as a spring after some months, and the amount of spring water is many times larger than that of the conventional one.
  • the reason that fish prefer to lay eggs in the shallow, gentle flow of spring water is that the temperature of the spring water hardly changes in summer and winter, the sunlight reaches the bottom, the supply of dissolved oxygen is sufficient, and organic matter flowing from the ground is easy. This is because plankton is fermented and decomposed, and is suitable for growing juveniles that feed on it. If there is no spring water, construct a horizontal boring that reaches the aquifer in the ground to create artificial spring water. The spring water will flow gently in the shallow water and flow into the dam lake via the fish collection pool. In addition, the structure shall be such that a torrent does not flow into the shallow ground so that eggs and fry in the shallow ground are not washed away by the flood.
  • the sluice of the cave fishway 26 b is opened, and the water of the fish collection pool 25 b flows into the dam lake, The body of the migratory fish feels the flow and stimulates the upstream instinct to swim toward the flow and return to the fish collection pool 25b.
  • the fishway floodgate 26a is opened, and the migratory fish goes up to the fish collection pool 25a through the submerged fishway 26a.
  • the migratory fish is moved upstream to the mountain stream flowing into the fish collection pool 25a, and then upstream to the fish collection pool (secondary dam) of the upstream dam.
  • dams in the main stream of the water system and the uppermost stream of many tributaries. For springs and tributaries flowing in the middle of the water system, dams will be built in stairs at those points so that the water can be stored at the highest possible point.
  • dams are divided into a high head group with a head of 500m or more between power plants at the foot of the mountain, a medium head group with a head of 500m to 30m, and a low head group with a head of less than 30m.
  • the middle drop group stores in a dam lake
  • the dam lake with a relatively large water capacity is designated as the lower pond of the Great Head Dam
  • the power plant with the large head is designated as the lower pond.
  • the power plant will be dredged deep and long along the riverbed at the foot of the mountain, and the power plant will be set up as a low head lower pond.
  • a large-diameter conduit is laid from each power plant to the vicinity of the most upstream dam, and as shown in Fig. 1, a number of dams around the dam are used to share a number of dams with one conduit.
  • the water pipe 1c and the water pipe 1a are connected via the drain valve 21.
  • the head is close to the water level in the headrace pipes of each group of large, medium and small, and the dam water level is from the highest altitude dam among the H1 or higher dams where the migratory fish can go upstream.
  • the above-mentioned valve 21 leading to the water pipe is opened and used for hydroelectric power generation, and is used up until the water level falls to H2, and then the valve of the dam having a high altitude and a water level of H1 or higher is opened and used for hydropower.
  • Hydraulic power generation will be stopped when power demand goes off-peak.
  • the surplus electric power is used to reverse the turbine and pump the water from the lower pond to raise the water level in the headrace.
  • H 1 When the water level of the dam is lower than H 1 and the valve of the dam close to the water level in the water pipe is opened, water is pumped until the water level of the dam reaches H 1, and when the water level reaches H 1, the valve is closed. Then, the water level of the water pipe is raised to the altitude of the dam where the altitude is low and does not reach H 1, and the valve of the dam is opened to pump water until the water level reaches H 1. Repeat this.
  • the sluice gate of the submerged fish passage 26b leading to the fish collection bull 25b downstream of the boulder flow prevention weir opens the water of the fish collection pool 25b into the dam lake.
  • the migratory fish senses the flow in the body, and the instinct is stimulated, swims toward the current, and travels up to the fish collection pool 25b through the cave fishway.
  • open the sluice gate of the cave fishway 26 Have a run up to a. Further, it is preferable that the mountain stream be moved up to reach the fish collection pool (secondary dam) of the upstream dam.
  • a gravel separation tank is provided between the headrace pipe and the power plant, and on the extension of the headrace pipe, sand is discharged to discharge the gravel separated by the gravel separation tank.
  • a pipe is provided, and water, gravel and organic matter sucked into the intake pipe are discharged through the water pipe by opening the drain valve, and further separated into water and organic matter and gravel in the gravel separation tank. It is desirable to discharge organic matter to the river via the turbine of the power plant, and to transport gravel to the gravel accumulation site via the sand drainage pipe.
  • sand drainage pipes 2 (2 a, 2 b) are installed on the extension of the water conveyance pipe 1 to separate the gravel into the sand drainage pipes 2.
  • the valve 19 at the end of the sand drainage pipe is closed, and flows along the inner wall of the gravel separation tank 11 without flowing into the sand drainage pipe. It is flipped out in a sand tube.
  • the width of the sediment lifting ring 9 should be equal to or greater than 3 m if the pipe is suspicious, so that the gravel will not rise and all the water leaving the pipe will flow under the ring. .
  • the sand 6 flowing down in a floating state generates a vortex 7 as shown by the arrow in Fig.
  • V Speed on circumference :: Radius of circular motion
  • Sand, silt, and clay have a specific gravity of about 2.6, so they accumulate on the side wall surface of the gravel separator tank 11, but the specific gravity of organic matter is not much different from water, so there is no ring while turning with water. Flows toward the center of the river, rises toward the headrace 1b, and is discharged to the river via a water turbine.
  • the organic matter released into the river is fermented and decomposed by the dissolved oxygen in the river to become inorganic nutrients, which breeds fish and shellfish, and does not cause ecosystem destruction by breaking the conventional food chain.
  • the gravel that has flowed into the sand drainage pipe does not flow during power generation because the valve 19 at the tip of the sand drainage pipe is closed, but is subjected to pressure vibration due to the reaction force of the water flow hitting the water turbine, and as a result, liquid And flows along the inclined surface, and is stored in the sand discharge pipe 2 a and the surge tank 18.
  • Sand removal is carried out when power generation is stopped during off-peak hours. The method is as follows: at the same time as power generation is stopped, the valve 19 at the tip of the sand discharge pipe 2b shown in Fig. 1 is opened, and the stationary gravel is rocked using the inertia (water hammer) of the water pipe that occurs when power generation is stopped. Fluidize and flow toward valve 19.
  • a surge tank 18 is installed to mitigate the impact of water hammer, from which it is branched into several small-diameter sand-discharge pipes 2 b from sand-discharge pipes 2 a, and gravel flows to multiple gravel-collection sites 20.
  • the water pipe 1a is branched, and the sand discharge pipe 2a is extended along the extension of the water pipe, and the water is guided upward to the turbine. It can be separated by a simplified sand and gravel separator that branches off the water pipe 1b.
  • the flow velocity is slow, the gravels wear is small, and the size of gravels to be separated is 1-3 mm.
  • the larger the size of the gravel the faster the rate of sedimentation in water. For example, the sedimentation velocity for a particle diameter of 1 mm is 10 cm Z seconds.
  • the gravel separation tank 11 as shown in Fig. 2 becomes unnecessary.
  • the flow velocity hitting the turbine is high when the head is large or large, and the particle size of the sand to be separated is 0.4 mm at the medium head, the sedimentation speed is 5 cm / sec, and the small head is 0.1 mm at the large head.
  • the sedimentation will slow down to 0.6 cm / sec due to the difference in sedimentation, and will flow down in a suspended state in the water pipe at a considerable rate. Therefore, a centrifugal separation device as shown in Fig. 2 is required.
  • the gravel to be separated will be almost in a sweeping state, and a simple type of gravel separator will be used. Can be separated.
  • the inner surface of the gravel separation tank 11 is rubber-lined as described below to prevent wear on the gravel, and the life of the gravel separation tank 11 can be made permanent.
  • Figure 3 is a cross-sectional view of the side wall of the gravel separation tank 11 and the lining of the sediment lifting ring 9. Since the side wall to which the sand is hit by centrifugal force wears the hardest, the thickness of the lining should be increased, and the lining thickness of the earth and sand floating prevention ring with less wear should be reduced.
  • a soft rubber lining sheet 12 as shown in Fig. 4 was manufactured, and the surface of the sheet in contact with the tank was unvulcanized beforehand, coated with colored urethane rubber, and then vulcanized to form a urethane rubber layer. Let it be.
  • the layer of colored urethane rubber 16 should be thick enough to withstand abrasion of gravel for more than one year.
  • the surface of the urethane rubber layer is adhered to the surface of the tank via a double-sided adhesive sheet 17.
  • a rubber sheet 13 containing reinforcing fibers is vulcanized and bonded to the end of the soft rubber lining sheet, and the rubber sheet containing the reinforcing fibers is fixed to the tank by a bolt and a nut 15.
  • FIG. 1 is a schematic diagram for explaining the hydroelectric power generation method of the present invention.
  • 2 (a) and 2 (b) are diagrams for explaining the operation of the gravel separation tank 11;
  • FIG. 2 (a) is a schematic plan view, and
  • FIG. 2 (b) is a schematic front view.
  • Figure 3 is an illustration of the lining inside the gravel separation tank.
  • FIG. 4 is an explanatory diagram of a method of connecting the lining sheets.
  • Fig. 5 is a schematic diagram showing a simple gravel separation device using a branch pipe of a water conveyance pipe.
  • Figure 6 shows the monthly discharge curve and the amount of hydroelectric power generated by rivers in the Hokuriku region.
  • Sediment and organic matter that flows down from the dam lake is preferentially sucked into the water pipe 1 c and merged into the large-diameter (usually 3 m diameter) water pipe 1 a via the drain valve 21, and water enters the turbine of the power plant
  • the gravel with a specific gravity of about 2.6 is separated in the gravel separation tank 11 by centrifugal force.
  • Organic matter having a specific gravity that is less than that of water is not separated and is flown to the drainage pipe 1b, which leads to the turbine, and to the lower pond for pumped storage and generation via the turbine. Even in the lower pond, sludge and organic matter are sucked by the intake pipe without being accumulated, and are discharged into rivers after hydroelectric power generation.
  • the gravel that has flowed into the sand discharge pipe 2a does not flow in the pipe because the valve 19 at the end of the sand discharge pipe is closed at the time of power generation, but due to the reaction force of the water flow hitting the turbine blades. Due to the pressure oscillation, the gravel liquefies, flows along the slope of the pipe toward surge tank 18 and is stored.
  • the diameter of the sand discharge pipe 2a is normally 3 m, and the sand discharge pipe 2 Use a sand pipe with a smaller pipe diameter than a. Its diameter should be about 60 cm to 1 m.
  • the intake pipe, the water pipe, and the sand discharge pipe used in the present invention be used in combination with the invention relating to a continuous lining method for a pipe joint and a pipeline proposed by the present inventors.
  • Patent No. 1 896 6144 “Piping joint structure”,
  • the length of the water pipe is several tens times longer than the conventional method.
  • the welding connection time of conventional steel pipes is 8 hours for 1 m diameter, and the connection time becomes longer in proportion to the outer diameter and pipe thickness, and it takes more than 30 hours for 80 mm pipe thickness at 3 m diameter, It takes a lot of cost and construction time for laying water transmission pipes. For this reason, the length of water transmission pipes (penstock) had to be reduced as much as possible.
  • connection time per pipe is 14 seconds, and even inexperienced persons can easily connect. Since the connection can be made, the connection cost and installation time are close to zero, and even if related works are included, the construction cost and time are several tenths.
  • the water transmission pipe (penstock) had to be shortened as much as possible by the conventional method, but if the above steel pipe joint is used, it is more economical to lengthen the water transmission pipe by several tens of times and maximize the head. It is.
  • the above-mentioned steel pipe joint has a self-sealing structure, does not leak even at high pressure, has elasticity and flexibility, and has a feature that it does not break even in a large earthquake of seismic intensity 6 or more.
  • Patent No. 16988219 Linepipe with laminated lining including adhesive re-material layer and method of construction
  • Japanese Patent Application No. 1 1 — 0 8 9 0 5 8 “The lining structure of the lining pipe and the method of removing the lining”
  • the gravel mixing rate is 6 times larger than the conventional one and the grain size is larger, so that the lower part of the pipe is 8 to 10 times larger than the conventional one. Wear out.
  • the flow velocity becomes more than ten meters per second, and the wear increases in proportion to the square of the flow velocity.
  • the current penstock has a thickness of as much as 15 mm and is used as a wear allowance. However, even in this case, it will be worn out in more than a year and turned into iron chips.
  • glass fiber reinforced polyester resin FRP pipes have a useful life of about half a year, beyond which the amount of wear increases and must be turned into industrial waste. No other wear measures can be used as well.
  • the continuous lining method can make the service life permanent. The construction method is to lay a pipeline of several kilometers with the above steel pipe joints, and to use flange joints at both ends.
  • a lining tube that is slightly shorter than that length is drawn into the pipeline, the lining is stretched and the length is adjusted, and then the tube is expanded and crimped by a big tube for continuous lining.
  • the lining tube is made of soft natural rubber, which is 12 times more wear-resistant than steel. Extrude the tube so that the lower thickness is 65 mm and the upper thickness is 8 mm.
  • the length of the tube is made slightly shorter than the length of the pipeline, and gaskets for sealing the flanges are vulcanized to both ends thereof.
  • an unvulcanized liquid urethane rubber is applied and cured by vulcanization. Thickness of the layer is gravel wear To withstand more than one year.
  • the colored urethane rubber layer is exposed due to wear of the lining tube, it is a warning that the lining needs to be replaced within one year. During that time, a new lining tube will be manufactured and preparations for replacement will be made. To replace it, peel off the adhesive at both ends of the pipe line, put the suction pipe of the vacuum pump into the tube, seal the ends of the tube and let the air out, then the tube will be crushed at atmospheric pressure. It is.
  • Hydropower uses only the water of the dams that can reach the migratory fish H1 or higher among many dams, and the water of the dams that do not reach the H1 water level is hydropowered until the H1 water level is reached. do not use. In this way, it is possible to minimize the invalid release of water beyond the dam dam during flooding, and to migrate migratory fish that have returned to the dam that has not reached the water level H1 as soon as possible to the fish collection pool of the upstream dam.
  • the water conduit has a curved part and a straight part. Since the centrifugal force of the fluid acts on the curved part, the steel pipe is fixed to the ground via the anchor block. Due to the high head, the flow velocity exceeds 10 meters per second, and local wear due to gravel occurs, so the radius of curvature should be 25 D or more (D: outside diameter of pipe).
  • D outside diameter of pipe
  • On the bend Uses a 1 m long pipe with a new steel pipe joint and uses a 12 m long flexible pipe. In the straight line part, hundreds of steel pipes of a fixed length are arranged in a straight line and connected by wire-jack connection.
  • a mixed forest with various vegetation mixed on both sides of the dam lake to create a riverside forest For example, trees with deep rooted trees (cedar, kunugi) and shallow rooted trees (cypress, beech) are mixed. Thus, even in the event of heavy rain, the spreading of the tree canopy relieves direct pressure on the soil, and understory vegetation and roots can stop the flow of soil flow. Planting mixed forests can prevent landslides. According to many experts, "mixed forests are clearly more effective at preventing landslides than simple forests. Forest soils are as soft as sponges and have the capacity to absorb and store precipitation. It suppresses surface water flowing into the dam lake, stores it in soil gaps, and moves to an underground aquifer. It also functions as a natural dam.
  • gravel that can be used as aggregate for concrete can be transported to a plain without hydroelectric power generation without using energy.
  • the original functions of the dam such as hydropower, pumped-storage, flood protection, water use, and sabo can be maintained forever.
  • dam lakes have become eutrophic, deteriorating the quality of tap water, containing moldy odor substances, and forced to drink tap water with reduced safety.
  • the reason is that harmful planktonic algae, plant inhabitants that cannot survive in a flowing state, begin to multiply when they become static.
  • the organic matter sludge
  • the dam lake is used up to the H2 water level close to the sky. Due to the fluidity, no eutrophication occurs and no harmful phytoplankton that grows only in still water. Phytoplankton generated in flowing water is harmless plankton, and it is eaten by the animal blankton that occurs at the same time, Sexual insects and fish are predated, an active food chain is maintained, and clear water quality is maintained ⁇ ? 0
  • Trihalomethanes are produced by the reaction of organic matter in raw tap water and chlorine added at the water treatment plant.
  • Alkali metabolism Decomposition products are trihalomethane-causing substances and are organic substances that are difficult to be decomposed by microorganisms.
  • the removal rate of microorganisms called activated sludge in ordinary sewage treatment plants is low, about 20%. .
  • This is an advanced treatment that combines the treatment of water purification plants and activated carbon.
  • the reduction rate is 60%, and if the trihalomethane-causing substances of Harunaga continue to increase as they are now, this effect will be reduced by half. Therefore, it is necessary to take countermeasures against emission sources, and since groundwater contains almost no methane-causing substance in the mouth of triha, studies are being conducted on methods of bringing it into sufficient contact with surface soil. In the hydroelectric power generation of the present invention, no trihalomethane-causing substances are generated. The reason is,
  • the dam lake At the time of hydropower generation, the dam lake is used up to the water level close to the sky, all the sludge is discharged, and at the time of off-peak power, water is pumped up, and the water of the dam lake is maintained at an appropriate nutrient concentration and is flowing. Therefore, no harmful planktonic algal plant blanks are generated.
  • boulders on the riverbed are crushed into gravel with a particle size of 60 mm or less, and organic matter is actively decomposed by microorganisms in the process of flowing water between the gravels, and trihalomethane-causing substances, which are difficult to decompose, are also decomposed.
  • the organic matter flowing down is preferentially sucked into the intake pipe and flows downstream without any residue, and is fermented and decomposed into inorganic nutrients by the natural purification action of the dissolved oxygen in the river, thereby forming an active food chain. It can be carried out and the catches can be restored to rich, old fishing grounds.
  • half of the 200 dams can store the same catchment basin area as large-scale dams.
  • the 200 dams will be built on the main stream of the river, and on the uppermost stream of many tributaries. So Then, many tributaries and springs to the power plant at the foot of the mountain will be built in a stepwise fashion to store spring water at high altitude. Then the average head of these dams will be three to six times that of large dams. Since the amount of power generation is proportional to (head) X (flow), the amount of hydroelectric power generation of the present invention is three to six times that of a conventional large-scale dam, and the power generation cost is lower than that of a large-scale dam.
  • the cost of power generation for conventional small-scale dams is more than 30 yen ZKWh, which is higher than 6 yen / KWh for thermal power generation, which is a major obstacle to the development of small-scale hydropower. .
  • the power generation cost is less than 3 yen / KWh, which is 1/10 that of a small dam. The reason is,
  • the hydropower generation system of the present invention requires a small length of a 3 m water intake conduit.
  • hundreds of small dams can be shared by water mains, power plants, and transmission facilities.
  • dam lake has no permanent sedimentation of sediment and sludge, and the functions of hydropower, pumped-storage, flood protection, irrigation, erosion control, and fish passages are permanently maintained. Depreciation is near zero.
  • the restricted water level method for flood control is a method in which water is released ineffective during the period when a flood is expected, the storage level is lowered to a certain level, and the capacity to control the flood is secured.
  • the hydroelectric power of the present invention creates hundreds of dams in one permanent system, it can store the entire amount of flood water and does not release any water. At that time, not only the dam lake, but also the underground aquifer, the water that has infiltrated from the revetment of the river method that is close to nature will be stored in the underground aquifer. It is possible to completely protect the flood protection function by completely storing the amount of water during the flood without any invalid release. When the water system encounters heavy rain, the withdrawal of surplus power is temporarily suspended and only flood protection works, and the withdrawal of surplus power during that time is only available for hydropower systems of other water systems not experiencing heavy rain. Have Lake Mu take over.
  • a submersible fishway is installed at each dam weir, and the combination of hydroelectric power generation and pumped-storage power generation allows fish with low upstream power to go up to the uppermost stream of the river.
  • a dam dam can be built downstream of the waterfall, and the dam water level can be raised to the top of the waterfall to help the ascent . If the range of migratory fish is expanded in this way, the fish population will increase in proportion to that, which is higher than that before the dam was constructed.
  • the fish that spawn at the upstream of the river and become fry will descend the river when they grow to some extent.
  • the water of a conventional dam lake flows slowly to the intake. Falling fish also leave themselves in the flow and get lost in the intake, undergoing severe pressure changes before and after passing through a hydroelectric turbine, and many of their fish rupture their internal organs and die.
  • the flow velocity at the inlet of the intake of the hydroelectric power generation of the present invention is about 5 m / sec or more, which is similar to that of flood.
  • a fish encounters a flow velocity comparable to that of a flood, it escapes at a rush speed and evacuates to a slow-moving rocky shadow or abyss It does not get lost in the intake.
  • the descending fish prefer a gentle flow, and when the dam water level falls and the sluiceway floodgate opens, it relies on that flow, heads towards the sloping fishway, and descends safely there.
  • the present invention also solves such a problem.
  • the small dam group of the present invention is used as the upper pond of pumped storage power generation, a lower pond is constructed downstream of the power plant, and the water in the lower pond can be pumped to the small dam group during off-peak hours, thereby solving this problem.
  • there is an advantage that migration of migratory fish can be performed smoothly when combined with pumping O
  • the existing large-scale dam was modified to have a structure suitable for the hydroelectric power generation method of the present invention, and the sediment of the dam lake was discharged, and the riverbed upstream of the dam was dredged to maximize the water storage efficiency.
  • the power control function and flood protection function can be maximized.
  • small-scale dams will be constructed upstream and downstream of the dam, and the dam will be used as a lower pond and upper pond for PSPP. If the characteristics of the steel pipe joints and the continuous lining method proposed by the inventor's prior proposal are used for the water conduit, the profit of the water conduit can be increased even if the length of the water conduit is tens of times longer than usual.
  • Wind power generation is proportional to the cube of wind speed, so it must be installed in a strong wind zone.
  • strong winds are often located on the summits and watersheds, and the cost of transporting construction materials and power transmission equipment is high, the amount of power generation is uneven, and power cannot be adjusted.
  • the present invention uses a cableway to transport construction materials and equipment to the uppermost stream of a river. If the cableway is extended to a watershed and a mountaintop in a strong wind zone and shared, the construction cost will be reduced. Power transmission equipment can also be used.
  • the small- and medium-scale dam using the hydroelectric power generation method of the present invention stores not only the water volume during the ⁇ water season but also the water volume during the flood season and floods for power generation, and the water volume is about three times that of the conventional type (Fig. 6). See).
  • the head is about five times that of the conventional type, and the amount of power generation is determined by the product of the amount of water and the head, so the amount of power generation is about 15 times.
  • the large-scale dam was converted to a new hydropower plant to discharge sediment and sludge from the dam lake, and further deeply dredged the riverbed upstream of the dam to increase the storage capacity many times. Eliminating the ineffective discharge of wastewater and relocating the power station further downstream to maximize the head will increase the power generation by many times compared to the conventional type.
  • the current technical development potential of large, medium and small scale hydropower is 129,840 GWh / year, which is 9 times 1,168,560 GWh / year, and fossil-fired thermal power generation can be completely abolished.
  • the use of hydrogen or fuel cell vehicles will become more widespread, and oil and natural gas will not have to be relied on overseas.
  • the world's technologically feasible hydropower is 227,785 GWh / year, 2,769,344 GWh / year during the existing construction, and the development rate is 19.5%. If this is adopted as a new hydropower method, the technically feasible hydropower will increase ninefold to 128,050,070 GWh / year.
  • the hydroelectric power generation method according to the present invention is spread around the world as a global standard (def act standard), global energy and environmental problems will be solved at once, and a sustainable development society will be realized. it can.
  • the present invention will receive the highest rating from the IS01400 series life cycle-assessment. That is, the hydroelectric power generation of the present invention can permanently maintain functions such as power regulation of dam lakes, flood protection, water use, sabo control, and securing of fish passages, and the service life of intake pipes, conduits, and sand discharge pipes It is permanent, generates electricity forever, and realizes a sustainable development society. Life cycle '. Assessment is a standard for pursuing methods to reduce the burden on the environment throughout the product life cycle from raw material extraction to disposal. The total energy consumed to build various power plants and the energy required to operate the plant using this method is taken as the input energy.
  • the value (output energy) / (input energy) is obtained by dividing the total amount of output energy obtained by operating the power plant by the input energy.
  • the highest value of (output energy) / (input energy) in the conventional method is 40 times for small and medium-sized hydropower. The lowest is solar power tripled.
  • the hydroelectric power generation of the present invention generates several tens of times the size of conventional small and medium-sized hydroelectric power generation at the same location and the same scale, has a permanent service life, has no recycling energy consumption, and (output energy) / (input energy). ) Can be thousands of times.
  • the hydroelectric power generation method of the present invention can transfer gravel to plains while generating hydroelectric power without using a huge amount of energy. Since power generation, flood protection, water use, sabo control, fishway access, etc. can be maintained forever, it is environmentally friendly, safe and economically advantageous.

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Abstract

A hydroelectric power generating method wherein during hydroelectric power generation, water is fed to the water wheel of an electric power station through a conduit pipe (1a) for electric power generation and the earth and sand and organic matter flowing down into a dam lake are discharged by being sucked through the intake ports of an intake pipe (1c) and branch pipe. The intake pipe (1c) is composed of a plurality of pipes connected by flexible pipe joints and the intake port at the front end of each pipe is movable to every corner of the lake bottom. The inner surface of each pipe is lined with a lining tube in the form of a tube of soft rubber having a colored urethane rubber layer placed on the outer peripheral surface of the tube. If the soft rubber wears out to expose the urethane rubber layer, preparations are made for replacement of the lining and the lining alone is replaced. The life of the intake pipes is extended forever, and the gravel can be conveyed to a plain by flow while generating hydroelectric power without using an enormous amount of energy. And, since the intrinsic functions of a dam, including hydroelectric power generation, pumped-storage power generation, flood prevention, irrigation, soil erosion control, and securement of regular courses for fish, can be maintained forever, the method is nature-friendly and safe and is very economically useful.

Description

明細 水力発電方法  Description Hydropower generation method

背景技術 Background art

a ) 発明の分野 a) Field of the invention

本発明は、 水力発電、 揚水発電、 洪水防御、 利水、 砂防、 魚道確 保などを永久に維持できる、 自然環境に優しく安全で経済的にも有 利な水力発電方法に関する。  TECHNICAL FIELD The present invention relates to a natural environment-friendly, safe, and economically advantageous hydroelectric power generation method that can permanently maintain hydroelectric power, pumped-storage power generation, flood protection, water use, sabo control, fishway security, and the like.

b ) 従来技術の説明 b) Description of the prior art

従来の大規模ダムの水力発電は、 流下する土砂でダム湖に堆砂し、 貯水量が年々減少し、 そのため電力調節、 洪水防御、 利水、 揚水発 電、 砂防などの諸機能が年々低下する。 また、 ダムは流下する有機 物を塞き止め、 食物連鎖の切断し、 生態系の破壊している。 即ち、 ダム湖を富栄養化し、 植物ブランク トンのァ才コを多発させ、 カビ 臭などの悪臭を放ち、 発癌性物質の 卜 リハロメタンを発生させ水道 水としての水質を低下させている。また、ダム下流を貧栄養化させ、 プランク トンを激減させ、 更にそれを餌にする魚介類を激減させ、 沿岸漁業を衰退させている。  In conventional large-scale dam hydropower, the sediment flowing down the lake dam sediments, and the amount of stored water decreases year by year.Therefore, various functions such as power regulation, flood protection, water use, pumping power generation, and sabo control decrease year by year. . Dams also block the flow of organic matter, break the food chain and destroy ecosystems. That is, eutrophication of dam lakes, frequent occurrence of plant blank tons, emission of odors such as mold odor, generation of carcinogenic substance trihalomethane, and deterioration of tap water quality. It also undermines the lower reaches of the dam, drastically reduces plankton, sharply reduces the amount of seafood that feeds on it, and reduces coastal fishing.

また、大規模ダムは広大な森林、農地、住宅地を水没させるなど、 流域住民の生活基盤を奪っている。 そのため流域住民や環境保護団 体の反対運動が激しく、 今後の大規模ダムの建設を著しく困難にし ている。  Large-scale dams have submerged vast forests, agricultural lands, and residential areas, depriving the basin residents of their livelihood. This has led to strong opposition from watershed residents and environmental protection groups, making the construction of large-scale dams extremely difficult in the future.

一方、 小規模なダムは数年でダム湖が埋まり、 これらダム湖の持 つ電力調節、 洪水防御、 利水、 砂防の諸機能は短期間に失われ、 晝 水期、 洪水時の水量は、 発電に使われずに無効放流されている。 こ れが発電コス 卜を高くする要因になり、 発電コス トは 3 0円 / K W hと石油火力発電の 6円/ K W hと比べ高く、 開発の障害になって いる。 またダムを建設すると土砂の海岸への流下が阻害され世界各 地で海岸の浸食が起きている。 On the other hand, small dams are buried in lakes in a few years, and their functions of power regulation, flood protection, water use, and sabo are lost in a short period of time. It is released without being used for power generation. This is a factor that raises the cost of power generation, and the cost of power generation is higher than 30 yen / KWh and 6 yen / KWh for oil-fired power generation, which is an obstacle to development. Also, when dams are constructed, the flow of sediment to the coast is hindered, and worldwide Coastal erosion is occurring on the ground.

さらに、 米国などでは土砂で埋まった大規模ダムをダムを破壊し て、 河川を元の状態に戻そうとする運動がある。 それはダムは回遊 魚の溯上を阻害し、 生息数を著しく減少させてきたからである。  In the United States and other countries, there is a movement to destroy large-scale dams filled with sediment and restore rivers to their original condition. Dams have prevented migration of migratory fish and have significantly reduced their populations.

また、 土石流災窖防止のため多くの砂防ダムが建設されているが、 数年で土砂で埋まり砂防ダムの機能を喪失している。 そのため、 土 砂に埋まつた砂防ダム上流で土石流が砂防ダムを乗り越え、 居住地 を襲い、 多くの人命を失う災害が世界各地で発生している。  Many sabo dams have been constructed to prevent debris flow disasters, but they have been buried in sediment in several years and have lost their function. As a result, debris flows over the sabo dam upstream of the sabo dam buried in sediment, attacking settlements and causing many lives in many parts of the world.

そこで、 発明者は、 これらの諸問題を解決する 「ダム施工方法お よび水力発電方法」 を、 特願 2 0 0 0— 2 6 5 6 0において提案し たが、 この先行提案発明においても次のよ な未解決な課題が残つ ていた。  Therefore, the inventor proposed “dam construction method and hydroelectric power generation method” to solve these problems in Japanese Patent Application No. 2000-265600. Unresolved issues such as

( 1 ) ダム湖の上流部に突出させた取水管で土砂および有機物は優 先的に吸引して下流に流し、 更にダム湖の上流部の河床を深く浚渫 して、 湖底が水平か逆勾配にして貯水効率 Q Z V ( Q :貯水量、 V : 堰堤体積) を最大にする必要がある。  (1) Sediment and organic matter are taken in preferentially by an intake pipe protruding upstream of the dam lake and flow downstream, and the riverbed upstream of the dam lake is deeply dredged. It is necessary to maximize the water storage efficiency QZV (Q: water storage volume, V: dam volume).

しかし、 河床には大小様々な巨礫が散在、 埋没している。 巨礫を 吸引すると、 導水管内の流速が著しく低下し、 また取水管、 導水管 および排砂管の途中で詰まる恐れがある。  However, boulders of various sizes are scattered and buried in the riverbed. If boulders are sucked, the flow velocity in the water pipe will be significantly reduced and clogging may occur in the intake pipe, water pipe, and sand discharge pipe.

( 2 ) 集中豪雨時には、 地山から大量の巨礫がダム湖に流れ込み、 巨礫が導水管を埋没させたり、 また導水管に吸い込まれる恐れがあ o  (2) During torrential downpour, a large amount of boulders may flow from the ground to the dam lake, and the boulders may bury the water pipe or be sucked into the water pipe.

( 3 ) 大規模ダムは、 殆どが多目的ダムであるが、 多目的の機能を 完全に果たしているダムは極めて少ない。 上流からの洪水を総て貯 留できるダムは僅かであり、 殆どが制限水位方式かまたは予備放流 方式 CT'あ 0 0  (3) Most large-scale dams are multipurpose dams, but very few dams fully fulfill multipurpose functions. There are only a few dams that can store all the floods from the upper reaches, and most of them are limited water level or pre-discharge type.

制限水位方式とは、 洪水が来ると予想される期間は放流して貯水 位を一定水位まで下げておき、 洪水を調節できる容量を確保してお く方式である。 この放流は無効放流で水力発電、 利水の両面からマ ィナス効果である。 The restricted water level method is to release water during the period when floods are expected to occur, lower the storage level to a certain level, and secure sufficient capacity to control floods. It is a method. This release is an ineffective release and has a negative effect from both sides of hydropower generation and water use.

—方、 予備放流とは出水が予想されたら、 短時間で貯水を放流し て貯水位を下げる方式である。 この放流も無効放流で、 水力発電、 利水両面でマイナス効果である。 また洪水時もピークカッ ト方式で 大量無効放流がされ、 下流部で本当に流量を減ら して欲しい時に流 量が減らないどいう問題がある。 超大型治水ダムでなければ、 洪水 の水量の全量を貯留する全量調節方式はできない。  On the other hand, preliminary discharge is a method in which when water is expected to flow out, the water is released in a short time to lower the water level. This release is also an invalid release, which has a negative effect on both hydropower and water use. Also, during the flood, a large amount of wastewater is released by the peak cut method, and there is a problem that the flow rate does not decrease when it is desired to reduce the flow rate in the downstream. Unless it is a very large flood control dam, it is not possible to have a full-fledged control system that stores the entire amount of flood water.

( 4 ) 発明者は、 特願 2 0 0 0— 3 6 2 6 3 1 において、 直線上の 長い導水管を沈砂池として機能させて、 導水管を流れ下る過程で分 離すべき砂礫の大部分を掃流状態にして、 導水管の延長線上の排砂 管に慣性力で流れ込ませ、 その上澄みを分岐させ、 水車に導水する 簡便な砂礫分離装置を提案した。  (4) In the Japanese Patent Application No. 2000-0-366 2 631, the inventor made most of the gravel to be separated in the process of flowing down the water pipe by making the long straight water pipe function as a sand basin. A simple sand and gravel separator was proposed, in which the stream was swept into the sand drainage pipe on the extension of the water pipe with inertia force, the supernatant was branched, and water was guided to the water turbine.

この先行提案は、 低落差で水車に当たる流速が遅い場合は適当で ある考えられる。 それは各種水車の摩耗データから低落差用水車の 分離すべき砂礫の粒径は 1 m m以上で、 その粒径の静水中沈降速度 は 1 O c m Z秒であり、 1 m m以上の砂礫は導水管流送中に掃流状 態になるので、 この簡便式砂礫分離装置で分離できるが、 中落差、 大落差では多くの砂が浮遊状態で流れるので砂礫の分離は十分でき なしヽ。  This prior proposal is considered appropriate when the flow velocity hitting the turbine due to low head is low. From the wear data of various turbines, the grain size of the gravel to be separated from the low head turbine is 1 mm or more, the sedimentation velocity of the still water of that grain size is 1 O cm Z seconds, and the gravel of 1 mm or more is Since it is in a sweeping state during transport, it can be separated by this simple type of gravel separator. However, in the middle and large heads, a large amount of sand flows in a floating state, and the gravel cannot be separated sufficiently.

( 5 ) 原子力発電、 風力発電、 地熱発電あるいは太陽光発電は、 発 電設備は電力需要変動に出力調節ができず、 オフピークには大量の 余剰電力が発生する。 その余剰電力を活用する揚水発電所の適地が 枯渴している。  (5) In nuclear power, wind power, geothermal power, or solar power generation, power generation equipment cannot adjust output to fluctuations in power demand, and a large amount of surplus power is generated during off-peak hours. Appropriate sites for pumped storage power plants that utilize the surplus power are dead.

( 6 ) ダム湖が富栄養化して植物ブランク トンの異常発生が起こり、 水道浄水場の濾過障害を起こしたり、 水道水の異臭問題を引き起こ している。 この原因はダム湖の湖底に沈積している有機物 (汚泥) が分解して大量の窒素、 リ ンが湖水に供給され、 植物プランク 卜ン を異常発生させている。 (6) Eutrophication of the dam lake has caused abnormal occurrence of vegetation blank tonnes, causing filtration problems at the water purification plant and offensive odor problems in the tap water. This is because organic matter (sludge) deposited on the bottom of the dam lake is decomposed and a large amount of nitrogen and phosphorus is supplied to the lake water, and phytoplankton Is abnormally occurring.

( 7 ) 水道水中の発癌性物質ト リハ口メタンの濃度が上昇傾向にあ り問題になっている。 それは水道原水に含まれる藻類の代謝 ■ 分解 産物などの有機物が原因物質となり、 浄水場で加えられる塩素と反 応して生成される。 ト リハロメタン生成能を有する代謝 , 分解產物 などの原因物質は短期間では分解されず、 蓄積される。  (7) The concentration of methane at the mouth of the carcinogen triha in tap water is on the rise and is a problem. It is caused by the metabolism of algae in raw tap water. ■ Organic substances such as decomposition products are the causative substances, and are produced in response to chlorine added at water treatment plants. The causative substances such as metabolites and decomposed substances having trihalomethane-producing ability are not decomposed in a short period of time and accumulate.

それ故に、 流入水量に比して貯水量の大きいダム湖は藻類の代 謝 ■ 分解産物物が蓄積して湖水のト リハロメタン生成能が高まり易 い。 ダム湖水の卜 リハロメタンの生成能の大きさを決める要因は、 藻類の増殖程度と水の回転率である。  Therefore, dam lakes, which have a large storage capacity compared to the inflow water, are likely to increase the trihalomethane production capacity of the lake water by accumulating decomposition products of algae. Factors that determine the trihalomethane production capacity of dam lake water are the degree of algae growth and water turnover.

この対策と して水力発電時にダム湖の汚泥を導水管で積極的に吸 引して排出し、 富栄養化を防止し藻類の異常発生を防止することの 他に、 湖水が流動して表層の土壌と十分に接触させることである。 それは地下水中には 卜 リハロメタン原因物質が含有されていないこ とから、 土壌は水中のフミン質を除去する能力を有していると思わ れている。  As a countermeasure, in addition to actively sucking and discharging sludge from the dam lake at the time of hydroelectric power generation with a water pipe, preventing eutrophication and preventing abnormal occurrence of algae, the lake water flows and the surface layer To make good contact with the soil. It is considered that the soil has the ability to remove humic substances in the water because the groundwater does not contain trihalomethane-causing substances.

ところで、 ダムの建設費は堤高の三乗に比例して高く なり、 例え ば、 堤高. 1 5 0 mの大規模ダムと堤高 2 0 mのダムを比較すると、 ( 1 5 0ノ 2 0 ) 3 = 4 2 2、 即ち、 堤高 1 5 0 mの大規模ダムを 1 箇所造る費用は、 堤高 2 0 mの小規模ダムを 4 2 2箇所造る費用と ほぼ同価格である.と言える。 By the way, the construction cost of the dam increases in proportion to the cube of the bank height. For example, comparing a large dam with a bank height of 150 m and a dam with a bank height of 20 m, (150 2 0) 3 = 4 2 2, that is, the cost of building one large dam with a height of 150 m is almost the same as the cost of building a small dam with a height of 20 m of 422 .

ただし、 在来型の小規模ダムは、 流下する土砂で短期間にダム湖 が埋もれてしまうので、 発電できる水量は渴水期の水量だけであり、 豊水期と洪水時の水量は無効放流され、 これが発電コス トを高くす る要因になっている。  However, in conventional small-scale dams, the dam lake is buried in a short period of time due to the flowing sediment, so the amount of water that can be generated is only the amount of water during the 渴 flood season, and the amount of water during the flood season and during the flood is invalidated. This is a factor that increases power generation costs.

本発明は、 このような小規模ダムを含めた在来型のダムによる発 電方式が抱える上記問題点を解消するためになされ、 その目的とす るところは、 膨大なエネルギーを使わずに、 水力発電をしながら砂 礫を平野部まで流送でき、 かつ、 ダム本来の機能である水力発電、 揚水発電、 洪水防御、 利水、砂防、 魚道確保等を永久に維持できる、 自然環境に優しく安全で経済的にも有利な水力発電方法を提案する とにある。 The present invention has been made to solve the above-mentioned problems of the power generation system using a conventional dam including such a small-scale dam, and the object thereof is to use a large amount of energy without using a huge amount of energy. Sand while hydropower The gravel can be transported to the plain and the permanent functions of the dam, such as hydroelectric power, pumped-storage power, flood protection, water use, sabo, and fishway access, can be maintained forever. To propose a new hydropower method.

発明の開示 Disclosure of the invention

そこで、 発明者は、 上掲の目的を実現するために鋭意研究した結 果、 以下の内容を要旨構成とする発明に想到した。 すなわち、  Therefore, as a result of earnest research to achieve the above-mentioned object, the inventor has come up with an invention having the following content as a summary. That is,

本発明は、 ダム湖の湖底にダム堰堤から上流部に延びる取水管を 設けると共に、 その先端に取水口を設け、 さらに取水管の途中にも ダム湖の湖底に沿って複数個の枝管を配設すると共に、 その先端に 取水口を設け、 一方、 前記取水管に排水弁を介して通じると共に、 ダム堰堤の下流側に導出されて発電所の水車に通じている導水管を 設け、 水力発電時には、 導水管から発電所の水車に水を供給して発 電すると共に、 ダム湖に流下する土砂や有機物を取水管および枝管 の取水口から吸引し排出するような水力発電方法において、  The present invention provides an intake pipe extending upstream from the dam dam at the bottom of the dam lake, an intake port at the tip thereof, and a plurality of branch pipes along the bottom of the dam lake in the middle of the intake pipe. At the same time, a water intake is provided at the tip of the water intake, and a water intake pipe is connected to the water intake pipe through a drain valve, and is provided downstream of the dam dam and connected to a turbine of the power plant. At the time of power generation, there is a hydroelectric power generation method in which water is supplied from a water pipe to a turbine of a power plant to generate electricity, and sediment and organic substances flowing down to a dam lake are sucked and discharged from intakes of water pipes and branch pipes.

前記取水管を可撓性を有する管継手を介して接続された複数の配 管から構成して、 各配管の先端の取水口を湖底の隅々まで移動可能 にすると共に、 各配管の内面を軟質ゴム製のチューブの外周面に着 色ウレタンゴム層を設けてなるライニングチューブでライニングし. 軟質ゴムが摩耗してウ レタンゴム層が露出したらライニングの取替 え準備を してライニングだけを取替えて、 取水管の耐用年数を永久 化することを特徴とする水力発電方法である。  The water intake pipe is composed of a plurality of pipes connected via flexible pipe joints, and the water intake at the tip of each pipe can be moved to every corner of the lake bottom, and the inner surface of each pipe is formed. Lining with a lining tube with a colored urethane rubber layer provided on the outer peripheral surface of a soft rubber tube. When the soft rubber wears and the urethane rubber layer is exposed, prepare the lining replacement and replace only the lining. This is a hydroelectric power generation method characterized by making the service life of an intake pipe permanent.

すなわち、 図 1 のように上流から流下する土砂や有機物を取水管 1 cの取水口 2 2 aおよび枝管取水口 2 2 bより吸引排出し、 土砂 や有機物は一切ダム湖に貯留させず、 小規模ダムでも電力調節、 洪 水防御、 利水、 砂防などの機能を永久的に果たさせるようにし、 ダ ム上流の河床 4を深く浚渫して湖底を水平が逆勾配になるようにし. 貯水効率 Q Z V ( Q : 貯水量, V : 堰堤体積) を大きく して費用対 効果を最大にするような水力発電方法である。 In other words, as shown in Fig. 1, sediment and organic matter flowing down from the upstream are sucked and discharged from the intake 22a of the water pipe 1c and the intake 22b of the branch pipe, and no sediment or organic matter is stored in the dam lake. Even small-scale dams can permanently perform functions such as power regulation, flood protection, water use, and sabo control, and deeply dredge the riverbed 4 upstream of the dam so that the horizontal bottom of the lake has a reverse slope. Efficiency QZV (Q: water storage, V: dam volume) It is a hydropower method that maximizes the effect.

図 1 において、 取水管 1 cに吸引された土砂は、 排水弁 2 1 を介 して大口径の導水管 1 a (通常 3 m怪) に合流できるようにし、 他 の多数のダムと導水管を共同利用して発電所まで導水される。  In Fig. 1, the sediment sucked into the intake pipe 1c is allowed to merge with the large-diameter water pipe 1a (usually 3m) through the drain valve 21 and is connected to many other dams and water pipes. The water will be led to the power plant by joint use.

在来方法の小規模ダムは、 たとえば、 図 6に示すような河川の月 毎の流量曲線から分かるように、 渴水期の水量では全水量の 1 / 3 しか使用できず、 その上、 落差の小さい発電しかできないが、 それ に対し本発明は、 ダム湖底に設けた取水管を、 排水弁を介して導水 管に繋ぐだけで落差が数倍 ( m倍とする) になり、 流量は 3倍であ るから発電量は 3 x m倍になり、 発電効率 Q H / V ( H : 落差) を 最大にすることができる。  As can be seen from the monthly discharge curve of a river, as shown in Figure 6, the conventional small-scale dam can use only 1/3 of the total water volume during the 渴 flood season, On the other hand, according to the present invention, by simply connecting the intake pipe provided at the bottom of the dam to the water pipe through the drain valve, the head becomes several times (m times) and the flow rate becomes 3 Therefore, the power generation will be 3 xm times and the power generation efficiency QH / V (H: head) can be maximized.

ダム湖の土砂や有機物を隅々まで吸引して排出するため、 取水管 の先端取水口 2 2 aおよぴ枝管 2 2 bにフロー 卜タンク 2 3を付け. 定期的にフ口ー トタンク内に圧搾空気を送って浮上させ、 圧榨空気 を噴射して、 その位置を変えて土砂堆積位置に沈設させる。 これら 操作はコンピューター制御と遠隔操作によって行うが、 この移動を 容易にするため、 取水管 1 cおよび枝管は、 後述するような可撓性 を有する鋼管継手で接続する。  Attach a float tank 23 to the water intake 22 a and the branch 22 b of the water intake pipe to suck and discharge all the soil and organic matter from the dam lake to every corner. Compressed air is sent to the inside to float, and compressed air is injected, changing its position and submerging it at the sediment accumulation position. These operations are performed by computer control and remote operation. To facilitate this movement, the intake pipe 1c and the branch pipes are connected by flexible steel pipe joints as described later.

上記水力発電を円滑に実施するために、 ダム建設前に予め河床 4 およびダム湖の湖底に埋没した巨礫を掘り起こし、砂利の大きさ(粒 怪 6 0 m m以下) までクラヅ シャ一で粉砕して取水管に吸引されや すくするか、 セメン トで固定しておく ことが望ましい。  Before the construction of the dam, the boulders buried in the riverbed 4 and the bottom of the dam lake were dug up before the construction of the dam, and crushed with a crusher to the size of gravel (up to 60 mm). It is desirable to be easily sucked into the intake pipe or fixed with cement.

砂礫の粒径 d ( m ) と、 流速により砂礫が流動し始める始動流速 V c ( m /秒) との関係は次式で表現される。  The relationship between the grain size d (m) of the gravel and the starting velocity V c (m / sec) at which the gravel starts flowing due to the flow velocity is expressed by the following equation.

V c = 4 . 0 ( d ) 1 / 2 V c = 4.0 .0 (d) 1/2

たとえば、 砂礫の径が 6 0 m mの場合、 V cは 1 . 0 mノ秒であ る。 取水口から離れると流速は距離の 3乗に逆比例して遅くなるが、 6 0 m m以下の径の砂礫なら取水口 2 2からある程度離れていても 吸引可能であり、 導水管 1 内の詰まりの恐れはなく 、 少ない流動抵 抗で流れ下り、 砂礫集積場まで流送可能である。 このような砂礫が 砂礫集積場まで流送された時、 篩分けだけでコンク リ— 卜骨材に利 用で For example, if the diameter of gravel is 60 mm, V c is 1.0 ms. When moving away from the intake, the flow velocity decreases in inverse proportion to the cube of the distance, but for gravel with a diameter of 60 mm or less, even if it is some distance from the intake 22 Suction is possible, and there is no risk of clogging in the water pipe 1, and it can flow down with a small flow resistance and can be transported to the gravel accumulation site. When such gravel is sent to the gravel accumulation site, it can be used for concrete aggregate only by sieving.

上記水力発電方法において、 ダム堰堤の下流側に集魚プールを設 けると共に、 その集魚プールからダム湖に通じる潜孔魚道を設け、 ダム湖の貯水を水力発電に使う場合は、 その水位が回遊魚が上流に 溯上可能な水位 H 1 以上に達した際には、 ダム湖の貯水を前記切換 弁を開いて導水管に流し、 その水位が前記集魚プールまで溯上して 来た魚が潜孔魚道を通って溯上可能な水位差 Δ hになるような水位 H 2になるまで使いきると同時に、 潜孔魚道の水門を開いて、 集魚 プールの魚を溯上させ、 水位差 Δ hがゼロになった時、 潜孔魚道の 水門を閉じるようにすることが望ましい。  In the above-mentioned hydroelectric power generation method, a fish pool is set up on the downstream side of the dam dam, and a submerged fishway is established from the fish pool to the dam lake. When the water reaches a water level H1 or more that can go upstream, the reservoir of the dam lake is opened through the diverter valve and drained into the water pipe, and the water level that goes up to the fish collection pool is lost. At the same time as the water level H2 is used up until the water level difference Δh that can go up through the hole fishway reaches H2, the sluice of the submerged fishway is opened, and the fish in the fish-collecting pool goes up and the water level difference Δh becomes It is desirable to close the sluice gate of the cave fishway when it reaches zero.

すなわち、図 1 に示すように、 ダム堰堤の下流側の集魚プール(副 ダム) 2 5 cまで溯上してきた魚を、 潜孔魚道 2 6 cを通ってダム 湖に溯上させる方法である。  In other words, as shown in Fig. 1, the fish that have gone upstream to the fish collection pool (secondary dam) 25c downstream of the dam embankment pass through the cave fishway 26c to the dam lake. .

そこで、 水力発電時は、 所定水位 H 2まで使い切る。 所定水位 H 2 とはダム堰堤の下流側に設置された集魚プール (副ダム) で溯上 して来た回遊魚が潜孔魚道を通って溯上できる水位差 Δ hである。 それは通常 0 . 2 mである。その時の潜孔魚道内の最大流速 V oは、 gを重力の加速度とし、 Δ hを落差として次式で求められる。  Therefore, at the time of hydropower generation, the water is used up to the predetermined water level H2. The predetermined water level H 2 is the water level difference Δh at which the migratory fish coming upstream from the fish collection pool (secondary dam) installed downstream of the dam dam can travel upstream through the submerged fishway. It is usually 0.2 m. The maximum velocity V o in the cave fishway at that time can be obtained by the following equation, where g is the acceleration of gravity and Δh is the head.

V o = ( 2 g - A h ) 1 / 2 V o = (2 g-A h) 1/2

ここで、 A hの落差とは、 ダムの水位と集魚プールの水位差であ る。 従って、 H 2は集魚プール (副ダム) の水位より上記の式で求 めた Δ hだけ高い水位をいう。 △ hを 0 . 2 mとして潜孔魚道の水 門を開けば、 潜孔魚道内の最大流速 V oは 2 m /秒となる。 回遊魚 が魚道を溯上する時は、 その魚の突進速度で溯上する。 その突進速 度は (魚の体長の 1 0倍) /秒である。 ただし、 突進速度は 6秒し か持続できない。 長時間持続可能の巡航速度は、 魚の体長の 2〜 4 倍/秒である。 それ故、 魚道内の流速は、 魚の突進速度より小さい 速度でなければならない。 潜孔魚道 2 6 cの水門を開く と集魚ブー ル 2 5 cの魚は体で流れを感じ溯上本能を刺激され、 流れに逆らつ て泳ぎ、 魚道を通って上のダム湖に溯上する。 Here, the head of A h is the difference between the water level of the dam and the water level of the fish collection pool. Therefore, H2 is the water level higher than the water level of the fish collection pool (secondary dam) by Δh calculated by the above equation. If h is 0.2 m and the sluice of the cave fishway is opened, the maximum velocity V o in the cave fishway will be 2 m / sec. When a migratory fish goes up the fishway, it goes up at the lunge speed of the fish. Its rush speed is (10 times the length of the fish) / sec. However, the charge speed is 6 seconds Or can't last. The long-lasting cruising speed is 2 to 4 times the length of the fish per second. Therefore, the flow velocity in the fishway must be lower than the fish rush speed. When the sluice gate of the cave fish passage 26c is opened, the fish of the fish catching bull 25c feels the flow in the body and stimulates the instinct to instinct, swims against the current and swims through the fishway to the upper dam lake. Up.

潜孔魚道 2 6 cを通った水は、 集魚ブール 2 5 cを経由して渓流 を通って、 更に下流側にあるダム堰堤の上流側に設けた集魚プール に流れ込み、 そこの魚の溯上本能も刺激して渓流を溯上させ、 更に その下流側ダム堰堤の潜孔魚道の水門を開き、 集魚プールの魚、 更 に卞流側ダ厶湖の魚も流れを体に感じて溯上本能を剌激され溯上を 開始することができる。  Water passing through the cave fishway 26 c flows through the mountain stream via the fish collection boule 25 c, and further into the fish collection pool located upstream of the dam dam on the downstream side. To stimulate the mountain stream, and open the sluice of the cave fishway at the downstream dam dam.The fish from the fish collection pool and the fish from Dam Lake, the side of the Byeon stream, also feel the flow and instinct to go upstream. Can be stimulated to start the run-up.

また、 上記水力発電方法において、 ダム湖の上流に巨礫流下防止 堰堤を造り、 その堰堤は、 粒径が所定値以下の砂礫および水をダム 湖に流し、 粒径が所定値を超えた巨礫や流木や木の枝は、 そこで塞 き止められるような縦長の切り目 (隙間) を有する構造とし、 さら に、 前記巨礫流下防止堰堤の上流側に集魚プールを設けると共に、 下流側にもダム湖に通じる他の集魚プールを設け、 また上流側集魚 プールと巨礫流下防止堰堤との間およびダム湖と前記他の集魚ブー ルとの間に、 それぞれ複数個の潜孔魚道とその水門を設けて、 その 水門を適時開閉することによって魚が上流と下流の両方向に行き来 できるようにすることが望ましい。  In addition, in the above hydroelectric power generation method, a boulder flow prevention dam is created upstream of the dam lake, and the dam flows gravel and water with a particle size of less than a predetermined value into the dam lake, and boulders with a particle size exceeding a predetermined value Driftwood and tree branches have vertical cuts (gap) so that they can be closed there. In addition, a fish collection pool is installed upstream of the boulder flow prevention weir, and a dam lake is also installed downstream. There will be other fish collection pools that communicate with each other, and a plurality of submarine fishways and their locks will be provided between the upstream fish collection pool and the boulder flow prevention dam and between the dam lake and the other fish collection bulls, respectively. It is desirable to open and close the sluice in a timely manner so that fish can move in both directions, upstream and downstream.

巨礫は定期的にクラッシャーで所定値以下の粒径に粉碎されて、 ダム湖に流下させるか、 ダム湖に流されないようにセメン トで固定 すること望ま しく、 それによつて、 豪雨時に巨礫がダム湖に流入す ることを効果的に防止することができる。  It is desirable that the boulders are periodically ground with a crusher to a particle size of less than a predetermined value and flow down to the dam lake, or fixed with cement so that they do not flow into the dam lake. It can be effectively prevented from flowing into the lake.

すなわち、 図 1 に示すように、 ダム湖の上流に巨礫流下防止用の 堰堤 2 4を配設し、 その堰堤には縦長の切れ目を形成して、 砂利以 下の粒径 ( 6 0 m m以下) の砂礫だけが、 切れ目を通って流下させ るよう〖こする。 In other words, as shown in Fig. 1, a dam 24 is installed upstream of the dam lake to prevent boulder flow, and a vertical cut is formed in the dam to reduce the particle size below the gravel (60 mm or less). Only the sand and gravel will flow down through the cut I'm sorry.

上記堰堤 2. 4で塞き止められた巨礫は、 定期的にクラッシャーで 砂利の大きさまで粉砕され、 堰堤に設置している潜孔魚道 2 6 aお よび 2 6 bを通ってダム湖に流下させるようにする。  The boulders blocked by the above dam 2.4 are periodically crushed to the size of gravel by a crusher and flow down to the dam lake through submerged fish passages 26a and 26b installed in the dam. Let it do.

また、堰堤 2 4は、下流に向かって突出した円弧状の堰堤を造り、 流下する巨礫が円弧の中央に集まるようにする。 その上流側には、 図 1 に示すように集魚プール 2 5 aを、 下流側には集魚プール 2 5 bを堰堤と一体構造に造ることが望ましい実施の形態である。  In addition, the embankment 24 will create an arc-shaped embankment projecting downstream, so that the boulders flowing down gather in the center of the arc. In this embodiment, it is desirable to form a fish pool 25a on the upstream side and a fish pool 25b on the downstream side as an integral structure as shown in Fig. 1.

集魚プールの 2 5 aと 2 5 bの間の堰堤 2 4の下部には、 潜孔魚 道 2 6 aを、 集魚プール 2 5 bとダム湖の間には、 潜孔魚道水門 2 6 bを複数か所設置する。 集魚プールは、 魚の生息に十分な水深を 常時保有できる構造にする。 洪水時は集魚プールは巨礫や土砂で埋 まり潜孔魚道の幾つかは機能しなくなつても、 堰堤の両端の潜孔魚 道は機能できるような構造にする。 集魚プールを埋めた巨礫は、 定 期的にクラッシャーで砂利の大きさまで粉砕して、 潜孔魚道 2 6 a、 集魚プール 2 5 b、 潜孔魚道 2 6 bを経由してダム湖に流す。 集魚 プール 2 5 bと地山の間に 3 0 c m前後の水深を常に保持し、 砂利 を敷き詰めた浅場を隣接させる。 そこに地山からの湧き水や支流を 流れ込ませ、 魚の産卵および稚魚の成育に理想的な環境を造ること ができる。  At the bottom of the dam 24 between the fish pools 25a and 25b, there is a diving fishway 26a, and between the fishing pool 25b and the dam lake, the diving fishway gate 26b Are installed at multiple locations. The fish collection pool should be constructed so that it always has sufficient depth for fish to live. In the event of a flood, the fishing pool will be filled with boulders and sediment, and some of the pits will not function, but the pits at both ends of the dam will be able to function. The boulders that fill the fish collection pool are periodically crushed to the size of gravel using a crusher, and then flow to Dam Lake via the pit cave 26a, the fish pool 25b, and the pit cave 26b. Always maintain a water depth of around 30 cm between the fish collection pool 25 b and the ground, and make a shallow field with gravel adjacent to the pool. The spring water and tributaries from the ground can flow into it, creating an ideal environment for spawning fish and growing fry.

本発明の水力発電は、 河川の最上流部から階段状にダムを造る方 式であり、 在来方に比べ何倍も多く地下の滞水層へ浸透している。 この滞水層の水は何か月後には再び河川に湧き水として戻ってく る , その湧き水量は在来方の何倍も多い。  The hydroelectric power generation of the present invention is a method in which a dam is built stepwise from the uppermost stream of a river, and the dam penetrates into the underground aquifer many times more than the conventional one. The water in this aquifer returns to the river again as a spring after some months, and the amount of spring water is many times larger than that of the conventional one.

これは地下の滞水層を地下のダムとして機能させていることにな り、 渴水期でも河川に水が流れる。 在来方のダムを造ると、 河川の 魚の生息数が激減する。 その原因の一つはダムの水位変動が大きく、 産卵に適した浅場が無くなるためである。 この理想的浅場を集魚プ ールの両岸側に造ることによって、 従来の問題は解決する。 This means that the underground aquifer functions as an underground dam, and water flows through the river even during the 渴 flood season. Building traditional dams will drastically reduce the number of fish in rivers. One of the reasons is that the water level of the dam fluctuates greatly and there is no shallow place suitable for spawning. This ideal shallow place The conventional problem is solved by building on both sides of the pool.

湧き水の流れ込む緩やかな流れの浅場を魚が好んで産卵するのは 湧き水の水温が夏冬殆ど変わらず、 太陽光が底まで達し、 溶存酸素 の供給も十分であり、 地山から流れ込む有機物が容易に発酵分解し、 プランク トンが繁殖しゃすく、 それを餌にする稚魚の成育に適して いるからである。 も し湧き水が無いときは、 地山の滞水層に達する 水平ボーリ ングを施工して人工的に湧き水を造る。 そして湧き水は 浅場を緩やかに流れ、 集魚プールを経由してダム湖に流れ込む構造 にする。 また、 浅場の卵や稚魚が洪水で流されないように浅場に激 流が流れ込まないような構造にする。 ダム湖の水位が回遊魚溯上可 能な水位 H 1 以上に達した時、 潜孔魚道 2 6 bの水門を開いて、 集 魚プール 2 5 bの水をダム湖に流し、 ダム湖の回遊魚の体に流れを 感じさせて溯上本能を刺激して流れに向かって泳がせ、 集魚プール 2 5 bに溯上させる。 次に魚道水門 2 6 aを開いて、 回遊魚を潜孔 魚道 2 6 aを通って集魚プール 2 5 aに溯上させる。 更に回遊魚を 集魚プール 2 5 aに流入する渓流に溯上させ、 上流のダムの集魚プ ール (副ダム) まで溯上させる。 その上流のダムの水が発電に使わ れ、 その水位が前記の H 2まで下がった時、 ダム堰堤に設置されて いる潜孔魚道の水門が開き、 回遊魚は上流のダム湖に溯上させる。 電力需要のオフピーク時には、 余剰電力で多数のダムに揚水し、 回遊魚を円滑に溯上させ、 また降下魚を安全に降下させるよう次の 方策を実施することが好ましい。  The reason that fish prefer to lay eggs in the shallow, gentle flow of spring water is that the temperature of the spring water hardly changes in summer and winter, the sunlight reaches the bottom, the supply of dissolved oxygen is sufficient, and organic matter flowing from the ground is easy. This is because plankton is fermented and decomposed, and is suitable for growing juveniles that feed on it. If there is no spring water, construct a horizontal boring that reaches the aquifer in the ground to create artificial spring water. The spring water will flow gently in the shallow water and flow into the dam lake via the fish collection pool. In addition, the structure shall be such that a torrent does not flow into the shallow ground so that eggs and fry in the shallow ground are not washed away by the flood. When the water level of the dam lake reaches the water level at which the migratory fish can reach the upstream, the sluice of the cave fishway 26 b is opened, and the water of the fish collection pool 25 b flows into the dam lake, The body of the migratory fish feels the flow and stimulates the upstream instinct to swim toward the flow and return to the fish collection pool 25b. Next, the fishway floodgate 26a is opened, and the migratory fish goes up to the fish collection pool 25a through the submerged fishway 26a. In addition, the migratory fish is moved upstream to the mountain stream flowing into the fish collection pool 25a, and then upstream to the fish collection pool (secondary dam) of the upstream dam. When the water of the upstream dam is used for power generation and the water level drops to the above H2, the sluice of the submarine fishway installed in the dam dam opens, and the migratory fish goes upstream to the dam lake . During off-peak hours of power demand, it is preferable to carry out the following measures so that surplus power can be pumped to a large number of dams to smoothly migrate migratory fish and safely descend fish.

①水系の本流および多数の支流の最上流部にダムを造る。 また水系 の途中で流れ込む湧き水や支流は、 その水を可能な限り標高の高い 地点で貯留できるよう、 その地点に階段状にダムを造る。  (1) Build dams in the main stream of the water system and the uppermost stream of many tributaries. For springs and tributaries flowing in the middle of the water system, dams will be built in stairs at those points so that the water can be stored at the highest possible point.

②これら多数のダムを、 山地の麓の発電所間の落差 5 0 0 m以上の 高落差グループ、 落差 5 0 0 m〜 3 0 mの中落差グループ、 3 0 m 未満の低落差グループに分ける。 中落差グループのダム湖の内で貯 水容量の比較的に大きいダム湖を大落差ダムの下池とし、 そこに大 落差の発電所を、 低落差のダム湖の内で貯水容量の比較的大きいダ ム湖を中落差の下池と して発電所を、 山地の麓の河川敷を深く長く 浚渫して、 そこを低落差の下池として発電所をそれぞれ設置する。 各発電所から最上流部のダムの近〈 まで大口径導水管を敷設し、 一 本の導水管に多数のダムを共同利用させるため、 図 1 に示すように その周辺の多数のダムの取水管 1 cと導水管 1 aとを前記排水弁 2 1 を介して繋ぐ。 ② These many dams are divided into a high head group with a head of 500m or more between power plants at the foot of the mountain, a medium head group with a head of 500m to 30m, and a low head group with a head of less than 30m. . The middle drop group stores in a dam lake The dam lake with a relatively large water capacity is designated as the lower pond of the Great Head Dam, and the power plant with the large head is designated as the lower pond. The power plant will be dredged deep and long along the riverbed at the foot of the mountain, and the power plant will be set up as a low head lower pond. A large-diameter conduit is laid from each power plant to the vicinity of the most upstream dam, and as shown in Fig. 1, a number of dams around the dam are used to share a number of dams with one conduit. The water pipe 1c and the water pipe 1a are connected via the drain valve 21.

③水力発電をする際は、 落差が大中小の各グループの導水管内の水 位に近く、 ダム水位が前記回遊魚が溯上可能な H 1 以上のダムの中 で最も標高の高いダムから、 導水管に通じる前記の弁 2 1 を開いて 水力発電に使用し、 水位が H 2まで下がるまで使い切り、 次に標高 が高く 、 水位が H 1 以上のダムの弁を開いて水力に使う。  ③ In the case of hydropower generation, the head is close to the water level in the headrace pipes of each group of large, medium and small, and the dam water level is from the highest altitude dam among the H1 or higher dams where the migratory fish can go upstream. The above-mentioned valve 21 leading to the water pipe is opened and used for hydroelectric power generation, and is used up until the water level falls to H2, and then the valve of the dam having a high altitude and a water level of H1 or higher is opened and used for hydropower.

ダム水位が H 2になると、 潜孔魚道 2 6 cの水門を開いて集魚プ ール 2 5 cまで溯上して来た回遊魚を潜孔魚道 2 6 cを通って溯上 させ、 同時に降下魚も降下させる。  When the water level of the dam reaches H2, the sluice gate of the cave fishway 26c is opened, and the migratory fish that has gone up to the fish collection pool 25c are made to go up through the cave fishway 26c. Let the descending fish descend.

④電力需要がオフピ一クになった時、 水力発電を停止する。 そして 余剰電力を使って水車を逆転させ、 下池の水を揚水して導水管内の 水位を上昇させる。 ダムの水位が H 1 より低く 、 導水管内の水位に 近いダムの弁を開いて、 そのダムの水位が H 1 に達するまで揚水し、 水位が H 1 になった時、 弁を閉じる。 そし,て次に標高が低く、 H 1 に達していないダムの標高まで導水管の水位を上昇させ、 そのダム の弁を開いて水位が H 1 に達するまで揚水する。 これを繰り返す。 水 Hydraulic power generation will be stopped when power demand goes off-peak. The surplus electric power is used to reverse the turbine and pump the water from the lower pond to raise the water level in the headrace. When the water level of the dam is lower than H 1 and the valve of the dam close to the water level in the water pipe is opened, water is pumped until the water level of the dam reaches H 1, and when the water level reaches H 1, the valve is closed. Then, the water level of the water pipe is raised to the altitude of the dam where the altitude is low and does not reach H 1, and the valve of the dam is opened to pump water until the water level reaches H 1. Repeat this.

⑤ダム水位が H 1 に達すると、 巨礫流下防止堰堤の下流の集魚ブー ル 2 5 bに通じる潜孔魚道 2 6 bの水門を開き、 集魚プール 2 5 b の水をダム湖に流す。 回遊魚はその流れを体で感じ、 溯上本能が刺 激され、 流れに向かって泳ぎ、 潜孔魚道を通って集魚プール 2 5 b に溯上させる。 次に潜孔魚道 2 6 aの水門を開き、 集魚プール 2 5 aに溯上させる。 更に渓流を溯上させて、 上流のダムの集魚プール (副ダム) に達するようにすることが好ましい。 ⑤ When the water level of the dam reaches H1, the sluice gate of the submerged fish passage 26b leading to the fish collection bull 25b downstream of the boulder flow prevention weir opens the water of the fish collection pool 25b into the dam lake. The migratory fish senses the flow in the body, and the instinct is stimulated, swims toward the current, and travels up to the fish collection pool 25b through the cave fishway. Next, open the sluice gate of the cave fishway 26 Have a run up to a. Further, it is preferable that the mountain stream be moved up to reach the fish collection pool (secondary dam) of the upstream dam.

さらに、 上記水力発電方法において、 導水管と発電所との間に砂 礫分離槽を配設すると共に、 導水管の延長線上には砂礫分離槽で分 離された砂礫を排出するための排砂管を配設し、 取水管に吸引され た水、 砂礫および有機物を、 前記排水弁を開いて導水管を介して排 出し、 さらに砂礫分離槽において水および有機物と砂礫とに分離し、 水および有機物を発電所の水車を経由して河川に放流すると共に、 砂礫を排砂管を介して砂礫集積所まで流送することが望ましい。 すなわち、 図 1 に示すように、 砂礫が混じった多数のダムの水を 大口径の導水管 1 (通常は 3 m径) に集め、 発電所の水車に入る前 で砂礫分離槽 1 1 を配設するとともに、 導水管 1 の延長線上に排砂 管 2 ( 2 a , 2 b ) を配設して、 砂礫を排砂管 2に分離する方法で ある。  Furthermore, in the above-mentioned hydroelectric power generation method, a gravel separation tank is provided between the headrace pipe and the power plant, and on the extension of the headrace pipe, sand is discharged to discharge the gravel separated by the gravel separation tank. A pipe is provided, and water, gravel and organic matter sucked into the intake pipe are discharged through the water pipe by opening the drain valve, and further separated into water and organic matter and gravel in the gravel separation tank. It is desirable to discharge organic matter to the river via the turbine of the power plant, and to transport gravel to the gravel accumulation site via the sand drainage pipe. In other words, as shown in Fig. 1, water from a number of dams mixed with gravel is collected in a large-diameter conduit 1 (usually 3 m in diameter), and a gravel separation tank 11 is distributed before entering the turbine at the power plant. At the same time, sand drainage pipes 2 (2 a, 2 b) are installed on the extension of the water conveyance pipe 1 to separate the gravel into the sand drainage pipes 2.

発電時は、 排砂管先端の弁 1 9は閉ざされ、 排砂管内には流れず に砂礫分離槽 1 1 の内壁に沿って流れるが、 掃流状態で流れ下った 砂礫は遠心力で排砂管内に弾き出される。 土砂浮上防止リ ング 9の 幅は、 導水管の怪が 3 mならそれに等しいか、 それ以上にして砂礫 が上昇しないようにし、 導水管を出た水は総てリ ング下に流れ込む ようにする。 浮遊状態で流れ下った砂 6は、 排砂管 2 との分岐部で 図 2の矢印のような渦流 7が生じ、 それに巻き込まれて排砂管内に 沈積する砂もあるが、 他は土砂浮上防止リ ング 9の下を砂礫分離槽 1 1 の側壁に沿って旋回し、 砂は下記の式で表される遠心力 f を受 け、 シル トや粘土と共に側壁表面に集積され、 塊状になって槽下部 に落ち排砂管内に入る。  At the time of power generation, the valve 19 at the end of the sand drainage pipe is closed, and flows along the inner wall of the gravel separation tank 11 without flowing into the sand drainage pipe. It is flipped out in a sand tube. The width of the sediment lifting ring 9 should be equal to or greater than 3 m if the pipe is suspicious, so that the gravel will not rise and all the water leaving the pipe will flow under the ring. . The sand 6 flowing down in a floating state generates a vortex 7 as shown by the arrow in Fig. 2 at the branch point with the sand discharge pipe 2, and some sand gets caught in it and deposits in the sand discharge pipe, but the others float up Swirl under the prevention ring 9 along the side wall of the gravel separation tank 1 1, and the sand is subjected to the centrifugal force f expressed by the following formula, and accumulates on the side wall surface together with silt and clay to form a block. To fall into the bottom of the tank and enter the sand discharge pipe.

f = m V ' / r  f = m V '/ r

m : 物体の質量  m: mass of the object

V : 円周上の速さ Γ : 円運動の半径 V: Speed on circumference :: Radius of circular motion

砂、 シル ト、 粘土の比重はほぼ 2 . 6であるから、 砂礫分離槽 1 1 の側壁表面に集積するが、 有機物の比重は水と大差ないので、 水 と共に旋回しながらリ ングの無い槽の中央に向かって流れ、 導水管 1 bに向かって上昇し、 水車を経由して河川に放流される。  Sand, silt, and clay have a specific gravity of about 2.6, so they accumulate on the side wall surface of the gravel separator tank 11, but the specific gravity of organic matter is not much different from water, so there is no ring while turning with water. Flows toward the center of the river, rises toward the headrace 1b, and is discharged to the river via a water turbine.

河川に放流された有機物は、 河川の溶存酸素で発酵分解され無機 の栄養塩になり、 魚介類を繁殖させ、 在来型の食物連鎖の切断によ る生態系破壊は起こらない。  The organic matter released into the river is fermented and decomposed by the dissolved oxygen in the river to become inorganic nutrients, which breeds fish and shellfish, and does not cause ecosystem destruction by breaking the conventional food chain.

—方、 排砂管内に流れ込んだ砂礫は、 発電中は排砂管先端の弁 1 9が閉ざされているので流れはないが、 水車に水流が当たる反力で 圧力振動を受け、 それにより液状化して傾斜面に沿って流動し、 排 砂管 2 aおよびサージタンク 1 8の貯留される。 それの排砂は、 電 力のオフピークで発電停止の際に行う。 その方法は、 発電停止と同 時に図 1 の排砂管 2 b先端の弁 1 9を開き、 発電停止時の起こる導 水管の慣性力 (水撃) を利用して静止している砂礫を揺り動かし、 流動化し弁 1 9に向けて流す。 水撃の衝撃を緩和するためにサージ タンク 1 8を設置し、 そこから排砂管 2 aより小径排砂管 2 b複数 本に分岐させ、 複数か所の砂礫集積場 2 0まで砂礫を流送し、 コン ク リ ー ト骨材と して使う。 これによりコンクリー ト骨材を動力を使 わずに消費地近く まで流送できる。 また海岸後退の問題も解決でき る ο  On the other hand, the gravel that has flowed into the sand drainage pipe does not flow during power generation because the valve 19 at the tip of the sand drainage pipe is closed, but is subjected to pressure vibration due to the reaction force of the water flow hitting the water turbine, and as a result, liquid And flows along the inclined surface, and is stored in the sand discharge pipe 2 a and the surge tank 18. Sand removal is carried out when power generation is stopped during off-peak hours. The method is as follows: at the same time as power generation is stopped, the valve 19 at the tip of the sand discharge pipe 2b shown in Fig. 1 is opened, and the stationary gravel is rocked using the inertia (water hammer) of the water pipe that occurs when power generation is stopped. Fluidize and flow toward valve 19. A surge tank 18 is installed to mitigate the impact of water hammer, from which it is branched into several small-diameter sand-discharge pipes 2 b from sand-discharge pipes 2 a, and gravel flows to multiple gravel-collection sites 20. To be used as concrete aggregate. This allows the concrete aggregate to be transported to near the consuming area without using power. It can also solve the problem of coastal retreat ο

低落差水車のように水車に当たる流速が遅く摩耗が軽微な場合は. 図 5のように導水管 1 aを分岐し、 導水管の延長線上に排砂管 2 a を、 上方に水車に向かう導水管 1 bを分岐した簡略型砂礫分離装置 で分離できる。 世界の水力発電の経験者の意見を総合すると、 低落 差の場合は流速は遅く、 砂礫摩耗は軽く、 分離すべき砂礫の粒径は 1 〜 3 m mと報告されている。 砂礫の粒径が大きい程、 水中の沈降 速度は速くなる。 例えば、 粒径 1 m mの沈降速度は 1 0 c m Z秒と なり、 掃流状態で流れ下り、 図 2のような砂礫分離槽 1 1 は不要に なる。 しかし中落差、 大落差になると水車に当たる流速が速く、 分 離すべき砂の粒径は中落差で 0 . 4 m m、 沈降速度は 5 c m /秒、 大落差では分離すべき 0 . 1 m mと小さ くなり、 沈降差で 0 . 6 c m /秒と遅く なり、 導水管内を相当な比率で浮遊状態で流れ下るの で、 図 2のような遠心力利用の分離装置が必要である。 When the flow velocity hitting the turbine is low and the wear is minimal, as in the case of a low head turbine. As shown in Fig. 5, the water pipe 1a is branched, and the sand discharge pipe 2a is extended along the extension of the water pipe, and the water is guided upward to the turbine. It can be separated by a simplified sand and gravel separator that branches off the water pipe 1b. According to the opinions of experienced hydropower users in the world, it is reported that in the case of low head, the flow velocity is slow, the gravels wear is small, and the size of gravels to be separated is 1-3 mm. The larger the size of the gravel, the faster the rate of sedimentation in water. For example, the sedimentation velocity for a particle diameter of 1 mm is 10 cm Z seconds. Then, it flows down in a bed condition and the gravel separation tank 11 as shown in Fig. 2 becomes unnecessary. However, the flow velocity hitting the turbine is high when the head is large or large, and the particle size of the sand to be separated is 0.4 mm at the medium head, the sedimentation speed is 5 cm / sec, and the small head is 0.1 mm at the large head. The sedimentation will slow down to 0.6 cm / sec due to the difference in sedimentation, and will flow down in a suspended state in the water pipe at a considerable rate. Therefore, a centrifugal separation device as shown in Fig. 2 is required.

ただし、 中落差でも乱流を生ずる湾曲部、 合流部がない直線状の 導水管長さが 7 0 0 m以上あれば、 分離すべき砂礫は殆ど掃流状態 になり、 簡略型の砂礫分離装置で分離できる。  However, if the length of the straight water pipe is 700 m or more with no curved section or junction where turbulence occurs even in the middle head, the gravel to be separated will be almost in a sweeping state, and a simple type of gravel separator will be used. Can be separated.

上記砂礫分離槽 1 1 の内面は、 下記のようにゴムライニングして 砂礫摩耗を防止し、 砂礫分離槽 1 1 の耐用年数を永久化することが できる。  The inner surface of the gravel separation tank 11 is rubber-lined as described below to prevent wear on the gravel, and the life of the gravel separation tank 11 can be made permanent.

図 3は、 砂礫分離槽 1 1 の側壁と土砂浮上防止リ ング 9のライ二 ング部の断面図である。 砂が遠心力で当たる側壁が最も激しく摩耗 するので、 ライニング厚さを厚く し、 摩耗の少ない土砂浮上防止リ ング面はラィニング厚さを薄くする。 図 4のような軟質ゴムライ二 ングシー ト 1 2を製作し、 そのシー トの槽に接する側の面は予め未 加硫.着色ウレタンゴムをコーティ ングし、 加硫してウレタンゴムの 層を形成させておく。 そして着色ウレタンゴム 1 6の層の厚さは 1 年以上砂礫の摩耗に耐える厚さにする。 そのウレタンゴム層の面を 両面粘着シ一 ト 1 7を介して槽の表面に粘着する。 また前記の軟質 ゴムライニングシー ト端部に強化繊維入りゴムシー ト 1 3を加硫接 着し、 その強化繊維内臓のゴムシ— 卜を槽にボル卜、 ナツ 卜 1 5で 締め付け固定する。 前記の軟質ゴムライニングシー 卜が摩耗して、 着色ウレタンゴムの層が露出した時、 前記と同様な方法で新しいラ イニングを製作し、取替え準備をする。摩耗ライニングの取替えは、 前記ポル ト ■ ナツ ト 1. 5で固着した部分を外し、 両面粘着シー トで 粘着した部分を引き剥がし、 前記の方法で新しいライニング . シー 卜を貼り付ける。 こう して砂礫分離装置の耐用年数を永久化する。 ライニング ■ シー 卜の材質は、 鉄鋼より 1 2倍ほど摩耗に強い軟質 天然ゴムを使う。 Figure 3 is a cross-sectional view of the side wall of the gravel separation tank 11 and the lining of the sediment lifting ring 9. Since the side wall to which the sand is hit by centrifugal force wears the hardest, the thickness of the lining should be increased, and the lining thickness of the earth and sand floating prevention ring with less wear should be reduced. A soft rubber lining sheet 12 as shown in Fig. 4 was manufactured, and the surface of the sheet in contact with the tank was unvulcanized beforehand, coated with colored urethane rubber, and then vulcanized to form a urethane rubber layer. Let it be. The layer of colored urethane rubber 16 should be thick enough to withstand abrasion of gravel for more than one year. The surface of the urethane rubber layer is adhered to the surface of the tank via a double-sided adhesive sheet 17. In addition, a rubber sheet 13 containing reinforcing fibers is vulcanized and bonded to the end of the soft rubber lining sheet, and the rubber sheet containing the reinforcing fibers is fixed to the tank by a bolt and a nut 15. When the soft rubber lining sheet is worn and the colored urethane rubber layer is exposed, a new lining is manufactured in the same manner as described above, and preparation for replacement is made. To replace the wear lining, remove the part that was secured with the Port ■ Nut 1.5, peel off the adhered part with a double-sided adhesive sheet, and use the new method described above. Paste the mouse. In this way, the useful life of the gravel separator is made permanent. Lining ■ The seat is made of soft natural rubber, which is 12 times more resistant to abrasion than steel.

図面の簡単な説明 BRIEF DESCRIPTION OF THE FIGURES

図 1 は、 本発明の水力発電方法を説明するための概略図である。 図 2 ( a )、 ( b )は、砂礫分離槽 1 1 の作用を説明する図であり、 図 2 ( a ) は概略的な平面図、 ( b ) は概略的な正面図である。 図 3は、 砂礫分離槽内のライニングの説明図である。  FIG. 1 is a schematic diagram for explaining the hydroelectric power generation method of the present invention. 2 (a) and 2 (b) are diagrams for explaining the operation of the gravel separation tank 11; FIG. 2 (a) is a schematic plan view, and FIG. 2 (b) is a schematic front view. Figure 3 is an illustration of the lining inside the gravel separation tank.

図 4は、 ライニング ' シ一 卜相互の接続方法の説明図である。 図 5は、 導水管の分岐管による簡易砂礫分離装置を示す概略図で める  FIG. 4 is an explanatory diagram of a method of connecting the lining sheets. Fig. 5 is a schematic diagram showing a simple gravel separation device using a branch pipe of a water conveyance pipe.

図 6は、 北陸地方の河川の月毎の流量曲線と水力発電水量を示す 図である。  Figure 6 shows the monthly discharge curve and the amount of hydroelectric power generated by rivers in the Hokuriku region.

発明を実施するための最良の形態 BEST MODE FOR CARRYING OUT THE INVENTION

以下、 本発明の水力発電方法を実施する好適な形態について説明 する。  Hereinafter, a preferred embodiment for carrying out the hydroelectric power generation method of the present invention will be described.

ダム湖から流下する土砂や有機物を取水管 1 cに優先的に吸引し 排水弁 2 1 を介して大口径 (通常 3 m径) 導水管 1 aに合流させ、 水が発電所の水車に入る前に、 比重がほぼ 2 . 6の砂礫を遠心力に よって砂礫分離槽 1 1 で分離させる。 比重が水と差の少ない'有機物 は分離されずに水車に通じる導水管 1 bと、 水車を経由して揚水発 電用の下池に流される。 下池でも汚泥、 有機物は堆積させずに取水 管で吸引され、 水力発電後、 河川に放流される。  Sediment and organic matter that flows down from the dam lake is preferentially sucked into the water pipe 1 c and merged into the large-diameter (usually 3 m diameter) water pipe 1 a via the drain valve 21, and water enters the turbine of the power plant Before that, the gravel with a specific gravity of about 2.6 is separated in the gravel separation tank 11 by centrifugal force. Organic matter having a specific gravity that is less than that of water is not separated and is flown to the drainage pipe 1b, which leads to the turbine, and to the lower pond for pumped storage and generation via the turbine. Even in the lower pond, sludge and organic matter are sucked by the intake pipe without being accumulated, and are discharged into rivers after hydroelectric power generation.

—方、 排砂管 2 aに流れ込んだ砂礫は、 排砂管先端の弁 1 9は発 電時は閉じているので管内の流れはないが、 水車の羽に水流が当た る反力による圧力振動があり、 それにより砂礫は液状化し、 管 傾 斜面に沿ってサージタンク 1 8に向かって流動し、 貯留される。  The gravel that has flowed into the sand discharge pipe 2a does not flow in the pipe because the valve 19 at the end of the sand discharge pipe is closed at the time of power generation, but due to the reaction force of the water flow hitting the turbine blades. Due to the pressure oscillation, the gravel liquefies, flows along the slope of the pipe toward surge tank 18 and is stored.

排砂管 2 aの管径は通常 3 mとし、 サージタンク 1 8で排砂管 2 aよ り管径の小さぃ排砂管にする。 その径は 6 0 c m〜 1 m ぐらい にする。 この弁を閉じる時も水撃が起こるが、 径が小さい程、 水撃 が小さ く 、 弁の開閉は容易である。 また弁を閉じる時は、 多数の弁 を同時に閉じるのではなく、 順次に閉じて水撃は緩和する。 The diameter of the sand discharge pipe 2a is normally 3 m, and the sand discharge pipe 2 Use a sand pipe with a smaller pipe diameter than a. Its diameter should be about 60 cm to 1 m. Although water hammer occurs when this valve is closed, the smaller the diameter, the smaller the water hammer and the easier it is to open and close the valve. Also, when closing the valves, rather than closing many valves at the same time, the valves are closed one after another to reduce the water hammer.

本発明に使う取水管、 導水管及び排砂管は、 本発明者が提案する 下記の 管継手とパイプラインの連続ライニング工法に関する発明 を組み合わせて使うことが望ましい。  It is desirable that the intake pipe, the water pipe, and the sand discharge pipe used in the present invention be used in combination with the invention relating to a continuous lining method for a pipe joint and a pipeline proposed by the present inventors.

( 1 ) 鋼管継手  (1) Steel pipe fittings

①特許第 1 9 8 6 1 4 4号、 「管継手構造」、  (1) Patent No. 1 896 6144, “Piping joint structure”,

②特願 2 0 0 0— 2 4 0 2 5 1 、 「管継手構造」 (2) Japanese Patent Application No. 2 0 0— 2 4 0 2 5 1, “Piping structure”

(特長)  (Features)

本発明では、 導水管の長さが在来方法の数十倍も長くなる。 在来 方法の鋼管の溶接接続時間は、 1 m径で 8時間、 外径、 管厚に比例 して接続時間は長くなり、 3 m径で 8 0 m m管厚では 3 0時間以上 もかかり、 導水管敷設の多額のコス 卜と工期がかかる。 そのために 導水管 (水圧鉄管) の敷設長さは極力短くせざるを得なかった。  In the present invention, the length of the water pipe is several tens times longer than the conventional method. The welding connection time of conventional steel pipes is 8 hours for 1 m diameter, and the connection time becomes longer in proportion to the outer diameter and pipe thickness, and it takes more than 30 hours for 80 mm pipe thickness at 3 m diameter, It takes a lot of cost and construction time for laying water transmission pipes. For this reason, the length of water transmission pipes (penstock) had to be reduced as much as possible.

上記の二つの先行提案発明は、 鋼管を数百本直線状に配列してヮ ィヤージャヅキで一括して圧入接続し、 一本当たりの接続時間は 1 4秒で接続可能で、 未経験者でも容易に接続できるので接続費と施 ェ時間はゼロに近く、 関連する工事を含めても、 工費とェ期は数十 分の一なる。 そうすると在来方法で導水管 (水圧鉄管) は可能な限 り、 短く しなければならなかったが、 上記鋼管継手を使えば導水管 を数十倍長く して落差を最大化する方が経済的である。 更に、 上記 鋼管継手は自封性構造で高圧でも漏洩せず、 伸縮性や可撓性があり、 震度 6以上の大地震でも破断しないという特長がある。  In the above two prior proposed inventions, several hundreds of steel pipes are arranged in a straight line and press-fitted and connected collectively with a wire jacket. The connection time per pipe is 14 seconds, and even inexperienced persons can easily connect. Since the connection can be made, the connection cost and installation time are close to zero, and even if related works are included, the construction cost and time are several tenths. In that case, the water transmission pipe (penstock) had to be shortened as much as possible by the conventional method, but if the above steel pipe joint is used, it is more economical to lengthen the water transmission pipe by several tens of times and maximize the head. It is. Furthermore, the above-mentioned steel pipe joint has a self-sealing structure, does not leak even at high pressure, has elasticity and flexibility, and has a feature that it does not break even in a large earthquake of seismic intensity 6 or more.

( 2 ) 連続ラィニング工法  (2) Continuous lining method

①特許第 1 6 9 8 2 1 9号 「粘着再材層を含む積層ライニングを 具えるラインパイプおよびその施工方法」 ②特願平 1 1 — 0 8 9 0 5 8 「ライニングパイプのライニング構 造およびラィニング取外し方法」 (1) Patent No. 16988219 "Linepipe with laminated lining including adhesive re-material layer and method of construction" ② Japanese Patent Application No. 1 1 — 0 8 9 0 5 8 “The lining structure of the lining pipe and the method of removing the lining”

③特願 2 0 0 1 - 2 0 5 3 7 4 「パイプライ ンのライニング方法 およびライニングの取替え方法」'  (3) Japanese Patent Application No. 2 0 0 1-2 0 5 3 7 4 “Method of lining pipe line and replacing lining”

(工法の概要と特長)  (Outline and features of the method)

本発明では、 ダム湖に流下する砂礫を積極的に吸引し排出すると、 砂礫混入率は在来より 6倍多く 、 かつ粒径が大きくなるため、 管下 部が上部の 8〜 1 0倍多く摩耗する。 また在来方法より高落差であ るため、 流速は毎秒十数メー トルになり、 摩耗は流速の二乗に比例 して増加する。 このため摩耗量は在来の数十倍摩耗し、 在来のどの 摩耗対策も半年で使えなくなる。 現状の水圧鉄管は 1 5 m mも管厚 みを厚く して摩耗代としているが、 こう しても一年余りで摩耗して 鉄屑になってしまう。  According to the present invention, if the gravel flowing down to the dam lake is actively suctioned and discharged, the gravel mixing rate is 6 times larger than the conventional one and the grain size is larger, so that the lower part of the pipe is 8 to 10 times larger than the conventional one. Wear out. In addition, because of the higher head than the conventional method, the flow velocity becomes more than ten meters per second, and the wear increases in proportion to the square of the flow velocity. As a result, the amount of wear is several tens of times the amount of conventional wear, and any conventional wear measures can no longer be used in six months. The current penstock has a thickness of as much as 15 mm and is used as a wear allowance. However, even in this case, it will be worn out in more than a year and turned into iron chips.

またガラス繊維強化ポリエステル樹脂の F R P管も耐用年数は半 年ぐらいであり、 それを超えると摩耗量が大きくなり産業廃棄物に せざるを得ない。 その他のいずれの摩耗対策も同様で使えない。 こ れ対して、上記連続ラィニング工法は、耐用年数を永久的にできる。 その工法は、 上記鋼管継手で数キロメー トルのパイブラィ ンを敷設 し、 その両端部はフランジ継手とする。  In addition, glass fiber reinforced polyester resin FRP pipes have a useful life of about half a year, beyond which the amount of wear increases and must be turned into industrial waste. No other wear measures can be used as well. In contrast, the continuous lining method can make the service life permanent. The construction method is to lay a pipeline of several kilometers with the above steel pipe joints, and to use flange joints at both ends.

その長さより少し短いライニングチューブをパイプライン内に引 き込み、 ライニング引き伸ばし長さ合わせして、 ビグでチューブを 拡管圧着する連続ライニングする方法である。 ライニングチューブ は鉄鋼より耐摩耗性が 1 2倍も優れている軟質天然ゴムを使う。 チ ュ一ブの下部厚さは 6 5 m m、 上部厚さは 8 m mになるように押し 出し成型する。 チュープの長さは前記パイプライン長さより少し短 く して、 その両端にフランジ部をシールするガスケヅ 卜を加硫接着 する。 このチューブ外周にプライマー塗布後、 未加硫で液状の着色 ウレタンゴムを塗布し、 加硫硬化させる。 その層の厚めは砂礫摩耗 に一年以上耐える厚さにする。 これを高強度の合成繊維製の補強シ 一 卜に包んで前記の既設パイプライ ン内に引き込む。 ライニングチ ュ―ブの先端に加硫接着しているガスケッ 卜をパイプライン端のフ ランジ面に合わせるため、 少し短めに製作せれたチューブを引き伸 ばして、 長さを合わせる。 その後、 チューブをビグで拡管して鋼管 面に圧着してライニングする。 In this method, a lining tube that is slightly shorter than that length is drawn into the pipeline, the lining is stretched and the length is adjusted, and then the tube is expanded and crimped by a big tube for continuous lining. The lining tube is made of soft natural rubber, which is 12 times more wear-resistant than steel. Extrude the tube so that the lower thickness is 65 mm and the upper thickness is 8 mm. The length of the tube is made slightly shorter than the length of the pipeline, and gaskets for sealing the flanges are vulcanized to both ends thereof. After applying a primer to the outer periphery of this tube, an unvulcanized liquid urethane rubber is applied and cured by vulcanization. Thickness of the layer is gravel wear To withstand more than one year. This is wrapped in a high-strength synthetic fiber reinforced sheet and drawn into the existing pipeline. In order to fit the gasket that has been vulcanized to the end of the lining tube to the flange surface at the end of the pipeline, stretch a slightly shorter tube and adjust the length. After that, the tube is expanded with a big tube and crimped to the steel pipe surface for lining.

ライニングチューブが摩耗して前記の着色ウレタンゴム層が露出 しれば、 1 年以内にライニングの取替えが必要であるとの警報であ るので、 その間に新しいライニングチューブを製作し取替え準備を 整える。 取替えは、 パイプライ ン両端の粘着部分を引き剥がし、 チ ュ―ブ内に真空ポンプのサクシヨンパイプを入れ、 チュ—プ両端を シールして中の空気を抜けば、 チューブは大気圧で押し潰される。  If the colored urethane rubber layer is exposed due to wear of the lining tube, it is a warning that the lining needs to be replaced within one year. During that time, a new lining tube will be manufactured and preparations for replacement will be made. To replace it, peel off the adhesive at both ends of the pipe line, put the suction pipe of the vacuum pump into the tube, seal the ends of the tube and let the air out, then the tube will be crushed at atmospheric pressure. It is.

これを捩じりながら下流側に引き出し、 同時に上流側より新しい ライニングチューブを引き入れて、 ライニングを取替える。 この様 にすれば、鋼管は全く摩耗してない.ので、耐用年数は永久的になる。 チューブ引入れ、 引出しに使つた補強シ— トも殆ど傷んでいないの で再利用できる。 また特に熟練を要せず、 小人数で高速のライニン グができるという特長を持っている。  Twist it out to the downstream side while pulling in a new lining tube from the upstream side to replace the lining. In this way, the steel pipe is not worn at all. The service life is permanent. The reinforcing sheet used for pulling in and pulling out the tube is almost intact and can be reused. It also has the feature that high-speed lining can be performed with a small number of people without special skill.

水力発電は、 多数のダムの内で回遊魚溯上可能水位 H 1以上のダ ムの水だけを使い、 H 1水位に達しないダムの水は、 H 1水位に達 するまでは水力には使わない。 こう して洪水時のダム堰堤を越える 無効放流を極力避けると共に、 水位 H 1 に達していないダムまで溯 上して来た回遊魚を出来るだけ早く上流側のダムの集魚プールに溯 上を可能にする。  Hydropower uses only the water of the dams that can reach the migratory fish H1 or higher among many dams, and the water of the dams that do not reach the H1 water level is hydropowered until the H1 water level is reached. do not use. In this way, it is possible to minimize the invalid release of water beyond the dam dam during flooding, and to migrate migratory fish that have returned to the dam that has not reached the water level H1 as soon as possible to the fish collection pool of the upstream dam. To

導水管路は湾曲部と直線部がある。 湾曲部は流体の遠心力が作用 するため、 アンカ一プロックを介して、 鋼管を地盤に固定する。 高 落差のため流速は毎秒十数メ— トルを越え、 砂礫による局部摩耗が 起こるので曲率半径は 2 5 D以上 ( D : 管外径) にする。 湾曲部に は 1 m長さ管を新鋼管継手で接続し 1 2 m長さの可撓管を使う。 直 線部分は定尺の長さの鋼管を何百本を直線状に配列して、 ワイヤ— ジャツキで一括圧入して接続する。 The water conduit has a curved part and a straight part. Since the centrifugal force of the fluid acts on the curved part, the steel pipe is fixed to the ground via the anchor block. Due to the high head, the flow velocity exceeds 10 meters per second, and local wear due to gravel occurs, so the radius of curvature should be 25 D or more (D: outside diameter of pipe). On the bend Uses a 1 m long pipe with a new steel pipe joint and uses a 12 m long flexible pipe. In the straight line part, hundreds of steel pipes of a fixed length are arranged in a straight line and connected by wire-jack connection.

ダム用道路を造るため森林伐採、山斜面の削取り、盛り土などで、 土砂が流失しやすくなる。 洪水があると川の水が真っ赤に濁り、 洪 水が収まっても慢性的な濁りが続く。 それが数年続く と、 渓流に棲 むカジ力など魚類、 水中昆虫などは繁殖が困難になり、 絶減状態に 陥る。 これを防止するために次の処置を講ずる。  Sediment is likely to be washed away by deforestation, mountain slope removal, embankment, etc. to build a dam road. Floods cause the river water to turn reddish and chronic turbidity continues even after the flood subsides. If this continues for several years, fish and underwater insects living in mountain streams, such as swordfish, will have difficulty breeding and fall into an extinct state. The following measures are taken to prevent this.

1 ) 工事用資機材の搬入は、 総て索道で行う。  1) All construction materials and equipment will be carried in by cableway.

2 ) ダム湖の両岸のコンク リー ト護岸は廃止して、 ドイツ、 スイス などで採用する自然に近い工法を採用する。 その工法は、 木の枝と 麻の紐で編んだ網で土を押さえ、 土砂の流失を止め、 そこに水草や 葦や湿地林を植え付けて根付かせる。 どんな草花をどの場所に植え るかは、 近隣の自然環境を一年以上調査して決めるが、 水辺を好む スゲ、 ヨシ、 水位変動に強いォ才バヤナギ、 ドロノキ、 ケャマハン ノキなどの湿地林などを植える。 木の枝や麻の紐が腐って土に還る 頃は、 植物の根が張り巡れされ、 土をしっかり捕らえて、 土砂の流 出を防止する。 2) The concrete revetment on both sides of the dam lake will be abolished and the method similar to nature used in Germany and Switzerland will be adopted. The method is to hold the soil with a net woven of tree branches and hemp strings, stop the runoff of sediment, and plant aquatic plants, reeds, and swamp forests there. What kind of flowers to plant in which location is decided by studying the surrounding natural environment for more than one year, but we recommend swamps, reeds, and swampy forests such as sedges, reeds, and mosses that are resilient to water levels. Plant. By the time the tree branches and hemp strings are rotten and returning to the soil, the roots of the plants are stretched around and the soil is firmly caught, preventing the flow of sediment.

3 ) ダム湖の両岸に各種の草木が混合した混交林を植林して河畔林 を造る。例えば深根性の木 (スギ、 クヌギ) と浅根性の木 (ヒノキ、 ブナ) の木を混植する。 これらより、 豪雨があっても樹木の樹冠の 広がりによって土壌への直接の圧力を和らげ、 また下層植生や根の 働きによって土流の流れを止めることができる。 混交林の植林は土 砂崩れを防止できる。 多くの専門家は、 「混交林が単純林より山崩れ 防止に明らかに有効である。 森林の土壌はスポンジのように柔らか く 、 降水を吸収し貯える能力をもっている。 集中豪雨にあっても直 接ダム湖に流れ込む表流水を抑え、 土壌の間隙に貯え、 更に地下の 滞水層に移動し、 何か月後、 湧き永として再び河川に流れ込み、 自 然のダムの機能も果たしている。 また水辺に張り出した枝からは落 葉のみならず多くの陸生昆虫が落下する。 河川内での落葉の流出が 進み、 水生昆虫の現存量が少なくなる夏の期間、 水辺林から落下す る陸生昆虫の量が逆にピークになる。 河川内が貧栄養状態のこの期 間、 落下昆虫は魚類の栄養を補う重要な食物源になる。」 と述べてい る 3) A mixed forest with various vegetation mixed on both sides of the dam lake to create a riverside forest. For example, trees with deep rooted trees (cedar, kunugi) and shallow rooted trees (cypress, beech) are mixed. Thus, even in the event of heavy rain, the spreading of the tree canopy relieves direct pressure on the soil, and understory vegetation and roots can stop the flow of soil flow. Planting mixed forests can prevent landslides. According to many experts, "mixed forests are clearly more effective at preventing landslides than simple forests. Forest soils are as soft as sponges and have the capacity to absorb and store precipitation. It suppresses surface water flowing into the dam lake, stores it in soil gaps, and moves to an underground aquifer. It also functions as a natural dam. In addition, many terrestrial insects as well as deciduous leaves fall from branches overhanging on the waterside. During summer, when litter discharge in rivers progresses and abundance of aquatic insects decreases, the amount of terrestrial insects falling from riparian forests peaks. During this period when the river is oligotrophic, falling insects are an important food source to supplement fish nutrition. " It has said

以上に述べたように、 この発明によれば、 現状の水力発電、 揚水 発電、 利水用水池、 砂防ダム、 魚道確保などが抱える総ての問題を 解決することができる  As described above, according to the present invention, it is possible to solve all the problems of the current hydroelectric power generation, pumped-storage power generation, irrigation water reservoirs, sabo dams, securing fishways, etc.

( 1 ) ダム湖の土砂の堆積は、 ダム機能を低下させるだけでなく、 多くの被害を与えている。 そして堆砂を取り除くため膨大なェネル ギ一が浪費されている。  (1) The sedimentation of the dam lake not only impairs the dam function but also causes a lot of damage. And huge amounts of energy are wasted to remove sediment.

本発明はエネルギーを使わずに、 水力発電を しながらコンクリー 卜の骨材に使える砂礫を平野部まで流送できる。 かつ、 ダムの本来 の機能である水力発電、 揚水発電、 洪水防御、 利水、 砂防を永遠に 維持できる。  According to the present invention, gravel that can be used as aggregate for concrete can be transported to a plain without hydroelectric power generation without using energy. In addition, the original functions of the dam, such as hydropower, pumped-storage, flood protection, water use, and sabo can be maintained forever.

( 2 ) 在来方法では上流から流下する有機物は、 大部分がダムで塞 き止められている。 そのためダム湖は富栄養化して水道原水の水質 が悪化させ、 カビ臭物質を含み、 安全性の低下した水道水の飲用を 余儀なく されている。 その原因は流れがある状態では生息すること ができない有害な浮遊性藻類の植物ブランク 卜ンが静水になると増 殖を始めるためである。  (2) In the conventional method, most organic matter flowing down from the upstream is blocked by dams. As a result, dam lakes have become eutrophic, deteriorating the quality of tap water, containing moldy odor substances, and forced to drink tap water with reduced safety. The reason is that harmful planktonic algae, plant inhabitants that cannot survive in a flowing state, begin to multiply when they become static.

本発明の水力発電では、 水力発電時は有機物 (汚泥) を優先的に 吸引して排出してダム湖が空に近い H 2水位まで使い切り、 才フピ —ク時は揚水され、 水は毎日流動しているので、 富栄養化は起こら ず、静水中にしか増殖しない有害な植物プランク トンは発生しない。 流動している水中で発生する植物プランク トンは無害なプランク 卜 ンであり、 同時に発生する動物ブランク 卜ンに捕食され、 それを水 性昆虫や魚が捕食し、 活発な食物連鎖が行われ、 清澄な水質が保た れ^? 0 In the hydroelectric power generation of the present invention, the organic matter (sludge) is preferentially sucked and discharged at the time of the hydroelectric power generation, and the dam lake is used up to the H2 water level close to the sky. Due to the fluidity, no eutrophication occurs and no harmful phytoplankton that grows only in still water. Phytoplankton generated in flowing water is harmless plankton, and it is eaten by the animal blankton that occurs at the same time, Sexual insects and fish are predated, an active food chain is maintained, and clear water quality is maintained ^? 0

( 3 ) 水導水中に発癌性物質卜 リハロメタンが年々増加し、 W H O (世界保険機構) が定める基準値 0 . O S m g Zリ ッ トルを越える 水道水が増え大きな問題になっている。 ト リハロメタンは水道原水 中の有機物と浄水場で加える塩素が反応して生成されたものである 流入量に比して貯水量の大きいダム、 即ち、 水の回転率が小さいダ ム湖がト リハ口メタン生成能が高まり易い。 また藻類の代謝 ' 分解 産物がト リハロメタン原因物質になり、 微生物によって分解されに く い有機物であって、 通常の下水処理場の活性汚泥という微生物で は除去率が低く、 2 0 %程度である。 現在行われている浄水場の才 ゾン処理と活性炭処理を加えた高度処理である。 しかし削減率は 6 0 %であり、 原永の 卜 リハロメタン原因物質が現状のように増加し 続ければ、 この効果は半減する。 そこで発生源対策が必要であり、 地下水中には ト リハ口メタン原因物質が殆ど含まれていないことか ら、 表層の土壌と十分に接触させる方法が研究されている。 本発明 の水力発電では ト リハロメタン原因物質の発生は皆無である。 その 理由は、  (3) The amount of carcinogen trihalomethane in the water conveyance increases year by year, and tap water exceeding the standard value of 0. 0 S Mg Z liter set by the World Health Organization (WHO) has increased and has become a major problem. Trihalomethanes are produced by the reaction of organic matter in raw tap water and chlorine added at the water treatment plant.A dam with a large storage capacity compared to the inflow, that is, a dam lake with a low water turnover rate, is a triha lake. Mouth production capacity tends to increase. Alkali metabolism Decomposition products are trihalomethane-causing substances and are organic substances that are difficult to be decomposed by microorganisms.The removal rate of microorganisms called activated sludge in ordinary sewage treatment plants is low, about 20%. . This is an advanced treatment that combines the treatment of water purification plants and activated carbon. However, the reduction rate is 60%, and if the trihalomethane-causing substances of Harunaga continue to increase as they are now, this effect will be reduced by half. Therefore, it is necessary to take countermeasures against emission sources, and since groundwater contains almost no methane-causing substance in the mouth of triha, studies are being conducted on methods of bringing it into sufficient contact with surface soil. In the hydroelectric power generation of the present invention, no trihalomethane-causing substances are generated. The reason is,

①水力発電時はダム湖が空に近い水位まで使い切り、 汚泥は残らず 排出され、 電力のオフピーク時は揚水され、 ダム湖の水は適正な栄 養塩濃度に保たれ、 かつ流動しているので、 有害な浮遊性藻類の植 物ブランク トンは発生しない。  ① At the time of hydropower generation, the dam lake is used up to the water level close to the sky, all the sludge is discharged, and at the time of off-peak power, water is pumped up, and the water of the dam lake is maintained at an appropriate nutrient concentration and is flowing. Therefore, no harmful planktonic algal plant blanks are generated.

②ダム湖の水位が下がった時、 自然に近い護岸工法で護岸の土壌は 大気と太陽光に晒され、 有機物の活発な分解が行われ、 また、 湖底 も溶存酸素と太陽光が行き渡り有機物の活発な分解が行われ、 難分 解性である 卜 リハロメタン原因物質も分解され無機栄養塩になる。 (2) When the water level of the dam lake falls, the seawall soil is exposed to the atmosphere and sunlight by virtue of a revetment method that is close to nature, and active decomposition of organic matter is carried out. Active decomposition occurs, and trihalomethane-causing substances, which are difficult to decompose, are also decomposed into inorganic nutrients.

③水位が上昇すれば分解された無機栄養塩は、 自然に近い河川工法 による護岸よ り土壌に浸透して護岸の植物や河畔林に肥料として吸 収され、 樹木を繁茂させる。 (3) When the water level rises, the decomposed inorganic nutrients penetrate the soil rather than revetment by the river construction method, which is close to nature, and are absorbed as fertilizer by revetment plants and riparian forests. Harvested and thriving trees.

④本発明の水力発電方法における階段状の多数のダム湖の水の約 2 割は、 自然に近い河川工法護岸や湖底より浸透して地下の滞水層に 貯留され、 何か月後に再び河川に湧き水となって戻ってく る。 その 地下永の移動過程で難分解性である 卜 リハロメタン原因物質の自然 浄化が行われる。  に お け る Approximately 20% of the water in the many step-like dam lakes in the hydroelectric power generation method of the present invention penetrates from the revetment and the bottom of the lake, which are close to nature, and is stored in the underground aquifer. It comes back as spring water. The natural purification of trihalomethane-causing substances, which are difficult to decompose, is performed in the process of moving underground.

⑤河川敷の巨礫は、 粒径 6 0 m m以下の砂礫に粉砕し、 その砂礫間 を水が流れる過程で有機物が微生物により活発に分解され、 難分解 性である トリハロメタン原因物質も分解される。  巨 The boulders on the riverbed are crushed into gravel with a particle size of 60 mm or less, and organic matter is actively decomposed by microorganisms in the process of flowing water between the gravels, and trihalomethane-causing substances, which are difficult to decompose, are also decomposed.

( 4 ) ナイル川にアスワンハイダムが建設された後、 ナイル河口の 漁獲量が 1 / 1 0に激減し、 デルタ地帯の農業は大量の化学肥料が 必要になった。 同じ現象が世界各地のダムで起こっておる。 これは 上流から流下する有機物がダムにより塞き止められ、 食物連鎖が切 断されるためである。  (4) After the construction of the Aswan High Dam on the Nile River, the catch at the Nile Estuary has dropped sharply to 1/10, and agriculture in the Delta has required large amounts of fertilizer. The same phenomenon is happening in dams around the world. This is because organic matter flowing from upstream is blocked by the dam and the food chain is cut.

本発明の水力発電方法では、 流下する有機物は取水管に優先的に 吸引 して残らず下流に流し、 河川の溶存酸素による自然浄化作用で 無機の栄養塩に発酵分解し、 活発な食物連鎖が行われ、 漁獲量を昔 の豊かな漁場に復活させることができる。  In the hydroelectric power generation method of the present invention, the organic matter flowing down is preferentially sucked into the intake pipe and flows downstream without any residue, and is fermented and decomposed into inorganic nutrients by the natural purification action of the dissolved oxygen in the river, thereby forming an active food chain. It can be carried out and the catches can be restored to rich, old fishing grounds.

( 5 ) 河川流域の理論包葳水力量に近付けることができる。 その水 系に大規模ダムを作った場合と比較し、 発電量を数倍に増加させ、 発電コス トを安くできる。 ダム建設費は堤高の三乗に比例して高く なる。 例えば堤高 1 5 0 mの大規模ダムの建設費は、 堤高 2 0 mの 小規模ダムを ( 1 5 0 / 2 0 ) 3 = 4 2 2箇所造るのとほぼ同じ費用 になる。 この小規模ダムを新水力発電のダム湖の湖底を水平が逆勾 配になるまで河床を深く浚渫すると、 その貯水量は堤高 1 5 0 mの 大規模ダムの貯水量の約 2倍になる。 即ち、 半分の約 2 0 0か所で 大規模ダムと同じ集水流域面積の水を分に貯水できる。 その 2 0 0 か所のダムを河川の本流、 多数の支流の最上流部にダムを造る。 そ して山地の麓の発電所までの間の多数の支流、 湧水を高き標高で貯 留するため階段状に多数のダムを造る。 そうすると、 これらダムの 平均落差は大規模ダムの落差の 3〜 6倍になる。 発電量は (落差) X (流量) に比例するので本発明の水力発電量は在来型大規模ダム の 3〜 6倍になり、 発電コス トは大規模ダムより安くなる。 一方、 在来型小規模ダムの発電コス 卜は 3 0円 Z K W h以上で、 火力発電 の 6円 / K W hと比較し高い、 これが小規模水力発電を開発する上 の大きな障害になっている。 (5) It can approach the theoretical hydropower of the river basin. Compared to a case where a large-scale dam is built in the water system, the amount of power generation can be increased several times and the cost of power generation can be reduced. Dam construction costs increase in proportion to the cube of the bank height. For example, the cost of constructing a large dam with a height of 150 m is about the same as building a small dam with a height of 20 m (150/20) 3 = 42. If this small dam is deeply dredged at the bottom of the new hydroelectric dam lake until the horizontal is inclined in reverse, the storage capacity will be about twice as large as that of a large dam with a bank height of 150 m. Become. In other words, half of the 200 dams can store the same catchment basin area as large-scale dams. The 200 dams will be built on the main stream of the river, and on the uppermost stream of many tributaries. So Then, many tributaries and springs to the power plant at the foot of the mountain will be built in a stepwise fashion to store spring water at high altitude. Then the average head of these dams will be three to six times that of large dams. Since the amount of power generation is proportional to (head) X (flow), the amount of hydroelectric power generation of the present invention is three to six times that of a conventional large-scale dam, and the power generation cost is lower than that of a large-scale dam. On the other hand, the cost of power generation for conventional small-scale dams is more than 30 yen ZKWh, which is higher than 6 yen / KWh for thermal power generation, which is a major obstacle to the development of small-scale hydropower. .

本発明の水力発電にすると小規模ダムの 1 / 1 0の 3円/ K W h 以下の発電コス トになる。 その理由は、  With the hydroelectric power generation of the present invention, the power generation cost is less than 3 yen / KWh, which is 1/10 that of a small dam. The reason is,

①在来型小規模ダムの水力発電は、 図 6のように渴水期の水量しか 発電に使えず、 豊水期、 洪水時の水量は無効放流されるが、 本発明 の水力発電はダム上流の河床を深く浚渫して貯水量を増大させ、 豊 水期、 洪水時の水量を総て発電に使い、 その水量は在来型の約 3倍 である。  (1) Conventional small-scale dam hydropower can be used for power generation only as shown in Fig. 6 (2) The amount of water used during the flood season can be used for power generation, and the amount of water used during floods and floods is discharged ineffectively. The riverbed is deeply dredged to increase the amount of water storage, and all the water used during the affluent and flood seasons is used for power generation, and the amount of water used is about three times that of conventional types.

②在来型小規模ダムは、 集水流域面積が狭く流量が少なく落差も 5 0 m ぐらいの地点でも、 本発明の水力発電では僅かの長さの取水用 導水管を 3 m佳の導水管に連結するだけで何十倍の落差と発電量が ③本発明の水力発電方式は、何百の小規模ダムが導水本管、発電所、 送電設備など共同利用できる。  (2) Even if the conventional small dam has a small catchment area, a low flow rate, and a drop of about 50 m, the hydropower generation system of the present invention requires a small length of a 3 m water intake conduit. (3) With the hydropower system of the present invention, hundreds of small dams can be shared by water mains, power plants, and transmission facilities.

④在来型小規模水力は発電だけの機能しかないが、 本発明の水力発 電は、 水力発電、 揚水発電、 洪水防御、 利水、 砂防、 魚道なで多機 能であり、 それぞれの受益者に建設費のァロケ—ション (費用割当) ができる。  小 規模 Conventional small-scale hydropower has only the function of power generation, but the hydropower generation of the present invention is multifunctional with hydropower, pumped-storage, flood protection, water use, erosion control, and fishery. A construction cost allocation (cost allocation) can be made.

⑤ダム湖は土砂と汚泥の堆積が永久的の起こらず、 水力発電、 揚水 発電、 洪水防御、 利水、 砂防、 魚道の諸機能を永久的に持続し、 導 水管も永久的に稼働し続けるので減価償却費はゼロに近い。 W ⑤The dam lake has no permanent sedimentation of sediment and sludge, and the functions of hydropower, pumped-storage, flood protection, irrigation, erosion control, and fish passages are permanently maintained. Depreciation is near zero. W

( 6 ) 在来型の大規模ダムは多目的であるが、 多目的の機能を十分 に果たしていない。 例えば洪水調節の制限水位方式は、 洪水が予想 される期間は無効放流して貯水位を一定水位まで下げ、 洪水を調節 できる容量を確保しておく方式である。 (6) Conventional large-scale dams are versatile, but do not fulfill their versatile functions. For example, the restricted water level method for flood control is a method in which water is released ineffective during the period when a flood is expected, the storage level is lowered to a certain level, and the capacity to control the flood is secured.

その一定水位を越える降雨があれば、 無効放流をする。 この無効 放流は水力発電と利水の立場からはマイナス効果である。 また洪水 時の洪水調節方式に一定量放流方式と一定率一定量放流方式がある , これは平野部の人家が密集している地帯の河川水位が上昇して、 水 量調節を最も して欲しい時に、 水量を下げられずダムの洪水防御を 十分に果たしていない。  If the rainfall exceeds the certain water level, the water will be released. This ineffective release has a negative effect from the standpoint of hydropower and water use. In addition, there are two types of flood control methods during floods: fixed-discharge method and fixed-rate constant-discharge method.This is because the river water level in the area where the houses in the plains are densely populated rises, and we want water control to be the highest. Occasionally, the water volume cannot be reduced and the flood protection of the dam has not been sufficiently achieved.

本発明の水力発電では一つの永系に何百のダムを造るので、 洪水 の全水量を貯留可能であり、 一切の無効放流はしない。 その時は、 ダム湖だけでなく地下の滞水層にも自然に近い河川工法の護岸から 浸透した水が地下の滞水層にも貯留することになる。 無効放流を一 切無く して洪水時の水量を総て貯留して洪水防御の機能を完全に果 たすことができる。 その水系が豪雨に会った時は、 余剰電力による 揚水は一時中断して、 洪水防御だけを機能させ、 その間の余剰電力 による揚水は、 豪雨に遭遇していない他の水系の水力発電方式のダ ム湖に肩代わり してもらう。  Since the hydroelectric power of the present invention creates hundreds of dams in one permanent system, it can store the entire amount of flood water and does not release any water. At that time, not only the dam lake, but also the underground aquifer, the water that has infiltrated from the revetment of the river method that is close to nature will be stored in the underground aquifer. It is possible to completely protect the flood protection function by completely storing the amount of water during the flood without any invalid release. When the water system encounters heavy rain, the withdrawal of surplus power is temporarily suspended and only flood protection works, and the withdrawal of surplus power during that time is only available for hydropower systems of other water systems not experiencing heavy rain. Have Lake Mu take over.

( 7 ) 本発明のように、 河川に多数のダムを階段状に造ると、 各ダ ムの貯水の 2 0 %ぐらいは地下に浸透して滞水層に貯留される。 そ の水は何か月後には再び湧水として河川に戻ってく る。 階段状ダム がなく、 鉄砲水となって渓流を流れ下る場合と比較して、 地下の滞 水層に浸透する量、 湧水量は共に何倍も多くなる。 湧水は夏冬の水 温の変化が殆どないので魚の産卵、 稚魚の成育に不可欠である。 ダ ム堰堤および巨礫流下防止堰堤の下流側の集魚プール (副ダム) の 両側の地山の間に水深 3 0 c mの砂利を敷き詰めた浅場を造る。 そ こに地山からの湧水や支流を導く。 そこは緩やかな流れがあり、 底 まで溶存酸素と太陽光が行き渡り、 地山から流れ込んだ有機物は発 酵分解して、 無機の栄養塩 (こなり稚魚の餌になるプランク トンを繁 殖させる。 魚はかかる場所に好んで産卵する。 それは稚魚の成育に 理想的な場所だからである。 湧き水は集魚プールや魚道を経由して ダム湖に流れ込み、 成長した稚魚も安全に降下できる。 魚の繁殖に 理想的な条件を揃えており、 ダム建設前より 、の生息数は増加する ことができる。 自然の河川の浅場は必ずしも理想的とは言えない。 そては、 自然の浅場は洪水に見舞われると、 産卵した卵や遊泳力.の 弱い稚魚が河口まで流され死滅することがあるからである。 (7) As in the present invention, when a large number of dams are formed in a river stepwise, about 20% of the stored water of each dam penetrates underground and is stored in the aquifer. The water will return to the river as a spring again some months later. Compared to a case where there is no step dam and flash floods flow down the mountain stream, the amount of seepage into the underground aquifer and the amount of spring water are both many times larger. Spring water has almost no change in water temperature in summer and winter, so it is indispensable for spawning of fish and growth of fry. A shallow field of 30 cm deep gravel will be created between the ground on both sides of the fish pool (secondary dam) downstream of the dam dam and boulder flow prevention dam. It guides springs and tributaries from the ground. There is a gentle flow there, the bottom Dissolved oxygen and sunlight spread throughout, and the organic matter that flowed from the ground fermented and decomposed to produce inorganic nutrients (plankton that could be used as bait for fry. Fish prefers to lay eggs in such places The spring water flows into the dam lake via the fish collection pool and the fishway, and the grown fry can safely descend.The ideal conditions for fish breeding are provided. The number of inhabitants can be increased before the construction of the dam The shallow waters of natural rivers are not always ideal, because the natural shallow waters are flooded with laid eggs and swimming power. This is because weak fry may be washed away to the estuary and die.

( 8 ) 在来型の殆どの大規模ダムには魚道が設置されていない。 そ れは設置には巨額の費用がかかり、 溯上魚も大きな標高差を溯上す るのは容易でないからである。 在来型中小規模のダム湖には魚道を 設置しているが、 溯上力の強い魚しか溯上できないという難点があ る  (8) Most conventional large dams do not have fishways. This is because the installation is very expensive, and it is not easy for upstream fish to return large altitude differences. A fishway is installed in a conventional small-to-medium-sized dam lake, but there is a drawback that only strong fish can go up

本発明の水力発電では、 各ダム堰堤に潜孔魚道を設置し、 水力発 電と揚水発電とを組み合わせて溯上力の弱い魚も河川の最上流部ま で溯上できる。 自然の河川では滝などがあると、 そこより上流には 溯上できないが、 本発明の水力発電では滝の下流にダム堰堤を造り、 ダム水位を滝の上端まで上昇させて溯上を助けることができる。 こ う して回遊魚の生息範囲を拡大すると、 それに比例して魚の生息数 も増加し、 ダム建設前の魚の生息数より増加する。  In the hydroelectric power generation of the present invention, a submersible fishway is installed at each dam weir, and the combination of hydroelectric power generation and pumped-storage power generation allows fish with low upstream power to go up to the uppermost stream of the river. In a natural river, if there is a waterfall, etc., it is not possible to go upstream from there, but with the hydroelectric power generation of the present invention, a dam dam can be built downstream of the waterfall, and the dam water level can be raised to the top of the waterfall to help the ascent . If the range of migratory fish is expanded in this way, the fish population will increase in proportion to that, which is higher than that before the dam was constructed.

( 9 ) 河川の上流で産卵して稚魚になった魚は、 ある程度に成育す ると川を降下する。 在来型のダム湖の水は緩やかな流れで取水口に 向かう。 降下魚もその流れに身を任せ取水口に迷い込み、 水力発電 の水車を通過する前後で猛烈な圧力変化を受け、 内臓が破裂して死 滅する魚が多くでる。 本発明の水力発電の取水口の入り口の流速は 5 m / s e c以上の洪水並の流速である。 魚は洪水並の流速に遭遇 すると、 突進速度で流れに逆らい流速の緩やかな岩影や淵に避難す る習性があり、 従って取水口に迷い込むことはない。 そして降下魚 は緩やかな流れを好み、 ダム水位が下がり、 潜孔魚道の水門が開い た時、 その流れに身を任せ、 潜孔魚道の方に向かい、 そこを通って 安全に降下する。 (9) The fish that spawn at the upstream of the river and become fry will descend the river when they grow to some extent. The water of a conventional dam lake flows slowly to the intake. Falling fish also leave themselves in the flow and get lost in the intake, undergoing severe pressure changes before and after passing through a hydroelectric turbine, and many of their fish rupture their internal organs and die. The flow velocity at the inlet of the intake of the hydroelectric power generation of the present invention is about 5 m / sec or more, which is similar to that of flood. When a fish encounters a flow velocity comparable to that of a flood, it escapes at a rush speed and evacuates to a slow-moving rocky shadow or abyss It does not get lost in the intake. And the descending fish prefer a gentle flow, and when the dam water level falls and the sluiceway floodgate opens, it relies on that flow, heads towards the sloping fishway, and descends safely there.

( 1 0 ) 土石流の多い河川では、 多数の砂防ダムを造り、 土石流災 害を防止しているが、 砂防ダムは数年の土砂で埋ま り、 砂防の機能 が失われている。 堆積土砂を掘削して、 ダンプカーで平野部の砂礫 集積場まで搬送することが一部で行われているが、 搬送用の道路建 設費と運送費に高額な費用がかかり、 採算性が悪く 、 あまり実施さ れていない。 そのため、 多額の費用をかけて砂防ダムを毎年新築し なければならない。 また、 砂礫の供給を絶たれた海岸は海岸の後退 が起こり、 これを防止するために、 護岸堤や離岸堤を毎年巨費を投 じて造り続けなければならない。  (10) In rivers with a lot of debris flow, numerous sabo dams have been built to prevent debris flow disasters, but sabo dams have been buried with sediment for several years, and the function of sabo has been lost. Excavation of sediment and sedimentation is carried out by a dump truck to transport it to a gravel accumulation site in the plain, but road construction and transportation costs for transportation are expensive, resulting in poor profitability. , Not very well implemented. Therefore, it is necessary to construct a new sabo dam every year at a high cost. In addition, coasts where the supply of gravel is cut off will cause coastal retreat, and in order to prevent this, seawalls and breakwaters must be continuously constructed at a huge investment every year.

この多数の砂防ダムは、 砂防だけの目的で造られているが、 これ を本発明の水力発電方法による多目的ダム、 即ち砂防の他に水力発 電、 揚水発電、 洪水防御、 利水、 魚道確保の諸機能を有するダムに 改造すれば上記の問題は総て解決する。 即ち、 山地が土砂崩れを起 こしても、 本発明の水力発電方法によって、 ダム湖をその湖底が水 平になるまで深く浚渫すれば、 土石流が堰堤を越えて下流に流れる ことは無く、 その土砂は水力発電時に取水管に吸引させて砂礫集積 場まで自動的に流送される。 その砂礫は、 コンク リ— 卜骨材に使つ たり、海岸の人工砂浜に使う。本発明の水力発電のダムの改造費は、 受益者にアロケーショ ン (費用割当) ができるので安くできる。 ( 1 1 )石油の枯渴と価格の暴騰に備えて、風力発電、太陽光発電、 原子力発電を一層增強しなければならない。 しかし、 これらの発電 は電力調節機能が無く、 オフピーク時には大量の余剰電力が発生す る。 その対策として大量の揚水発電所を建設しなければならないが、 大規模揚水発電の上池の適地が開発し尽く されて適地が数少なく な つている。 Many of these sabo dams are constructed solely for the purpose of sabo control, but this is a multipurpose dam using the hydroelectric power generation method of the present invention. All the above problems can be solved if the dam is modified to have various functions. In other words, even if a landslide occurs in the mountains, if the dam lake is deeply dredged until the bottom of the dam becomes horizontal by the hydroelectric power generation method of the present invention, the debris flow will not flow downstream over the weir, At the time of hydropower generation, the water is sucked into the intake pipe and automatically sent to the gravel accumulation site. The gravel is used for concrete aggregate and for artificial sand on the coast. The renovation cost of the hydroelectric dam of the present invention can be reduced because the beneficiaries can be allocated (cost allocation). (11) Wind power, solar power and nuclear power must be further strengthened in preparation for oil depletion and price spikes. However, these generations do not have a power regulation function and generate a large amount of surplus power during off-peak hours. As a countermeasure, a large number of pumped storage power plants must be constructed.However, suitable sites for the upper pond of large-scale pumped storage power plants have been developed and few suitable sites are available. I'm wearing

本発明はこのような問題も解決する。 即ち、 本発明の小規模ダム 群を揚水発電の上池とし、 発電所下流に下池を造り、 オフピーク時 に下池の水を小規模ダム群に揚水できて、 この問題が解決される。 更に揚水と組み合わせると回遊魚の溯上が円滑に行われる利点があ る O  The present invention also solves such a problem. In other words, the small dam group of the present invention is used as the upper pond of pumped storage power generation, a lower pond is constructed downstream of the power plant, and the water in the lower pond can be pumped to the small dam group during off-peak hours, thereby solving this problem. Furthermore, there is an advantage that migration of migratory fish can be performed smoothly when combined with pumping O

( 1 2 ) 既存の大規模ダムを本発明の水力発電方法に適した構造に 改造して、 ダム湖の堆積土砂を排出し、 更にダム上流の河床も浚渫 して、 貯水効率を最大化して、 電力調節機能、 洪水防御機能を最大 にできる。 更に、 そのダムの上流と下流に小規模ダムを造り、 その ダムを揚水発電の下池および上池にする。 それに使う導水管は、 発 明者の先行提案にかかる鋼管継手と連続ライニング工法の特長を導 水管に生かすと、 導水管長さが在来よい何十倍も長くても採算が合 ラ o  (12) The existing large-scale dam was modified to have a structure suitable for the hydroelectric power generation method of the present invention, and the sediment of the dam lake was discharged, and the riverbed upstream of the dam was dredged to maximize the water storage efficiency. The power control function and flood protection function can be maximized. In addition, small-scale dams will be constructed upstream and downstream of the dam, and the dam will be used as a lower pond and upper pond for PSPP. If the characteristics of the steel pipe joints and the continuous lining method proposed by the inventor's prior proposal are used for the water conduit, the profit of the water conduit can be increased even if the length of the water conduit is tens of times longer than usual.

( 1 3 ) 風力の発電量は風速の三乗に比例するので強風地帯に設置 しなければならない。 ところが強風地帯は山頂や分水嶺上が多く、 そこまで建設資材を搬入したり、 送電設備に多くの費用がかかり、 発電量にムラが多く、 電力調節ができないなど欠点が開発促進の障 窖になっている。 本発明は河川の最上流部まで索道を使って建設資 材ゃ器材を搬送しており、 これを強風地帯の分水嶺および山頂まで 索道を延長して、 共用すれば建設費は安く なる。 また送電設備も共 用できる。  (13) Wind power generation is proportional to the cube of wind speed, so it must be installed in a strong wind zone. However, strong winds are often located on the summits and watersheds, and the cost of transporting construction materials and power transmission equipment is high, the amount of power generation is uneven, and power cannot be adjusted. ing. The present invention uses a cableway to transport construction materials and equipment to the uppermost stream of a river. If the cableway is extended to a watershed and a mountaintop in a strong wind zone and shared, the construction cost will be reduced. Power transmission equipment can also be used.

オフピーク時の余剰電力を使って揚水をすれば風力発電の欠点は 総て取り除かれ、 開発が促進される。  Pumping with excess off-peak surplus power will remove all the drawbacks of wind power and promote development.

( 1 4 ) 水力発電の未開発だけでなく、 既設 ■ 工事中の水力発電を も本発明の水力発電方法に改良すれば、 化石燃料の火力発電を全廃 でき、 石油などのエネルギー枯渴と地球温暖化等の問題が一挙に解 決できる。 世界の水力発電の潜在力の資料、 『 Internati onal Water Power & Dam Construction Yearbook (1997)』 によれば、 日本の技 術的に開発可能水力は 129,840 GWh/年、 既設 ■ 工事中は 91,654GWh/ 年、 開発率 7 0. 6 %と報告されている。 それは本発明の水力発電 方法による中小規模ダムは、 渴水期水量だけでなく豊水期、 洪水時 の水量を総て貯留して発電に使い、 その水量は在来型の約 3倍 (図 6参照) になる。 落差は平均して在来型の約 5倍になり、 発電量は 水量と落差の積で決まるので、 発電量は約 1 5倍になる。 大規楱ダ ムを新水力発電に改造してダム湖の堆砂と汚泥を排出し、 更にダム 上流の河床を深く浚渫して貯水量を何倍にも増大させ、 洪水調節に 伴う無効放流、 排砂のための無効放流を絶無にし、 発電所位置を更 に下流に移設して落差を最大化すると、 発電量は在来型の何倍も増 大できる。 (14) Not only undeveloped hydropower, but also existing ■ If hydropower during construction is improved to the hydropower method of the present invention, fossil-fired thermal power generation can be completely abolished, and the depletion of energy such as oil and the earth Issues such as global warming can be solved at once. Data on the potential of global hydropower, Internati onal Water According to the Power & Dam Construction Yearbook (1997), Japan's technically feasible hydropower is 129,840 GWh / year, and it is already installed. ■ During construction, 91,654 GWh / year and the development rate is reported to be 70.6%. I have. The reason is that the small- and medium-scale dam using the hydroelectric power generation method of the present invention stores not only the water volume during the 渴 water season but also the water volume during the flood season and floods for power generation, and the water volume is about three times that of the conventional type (Fig. 6). See). On average, the head is about five times that of the conventional type, and the amount of power generation is determined by the product of the amount of water and the head, so the amount of power generation is about 15 times. The large-scale dam was converted to a new hydropower plant to discharge sediment and sludge from the dam lake, and further deeply dredged the riverbed upstream of the dam to increase the storage capacity many times. Eliminating the ineffective discharge of wastewater and relocating the power station further downstream to maximize the head will increase the power generation by many times compared to the conventional type.

大中小規模水力の技術的開発可能電力の現状の 129,840GWh/ 年は 9倍 1,168,560GWh/年になり、 化石燃料の火力発電の全廃は可能で あり、 低廉な電力により大量の水素ガスが得られ、 水素ガスまたは 燃料電池の自動車が一層普及し、 石油、 天然ガスを海外に依存しな くて済む。 これを世界規模で観ると、 世界の技術的開発可能の水力 は ,227,785 GWh/ 年、 既設■ 工事中は 2,769,344 GWh/ 年、 開発 率 1 9 . 5 %である。これを新しい水力発電方法として採用すれば、 技術的開発可能の水力は 9倍の 128,050,070 GWh/ 年、 になる。  The current technical development potential of large, medium and small scale hydropower is 129,840 GWh / year, which is 9 times 1,168,560 GWh / year, and fossil-fired thermal power generation can be completely abolished. However, the use of hydrogen or fuel cell vehicles will become more widespread, and oil and natural gas will not have to be relied on overseas. Looking at this on a global scale, the world's technologically feasible hydropower is 227,785 GWh / year, 2,769,344 GWh / year during the existing construction, and the development rate is 19.5%. If this is adopted as a new hydropower method, the technically feasible hydropower will increase ninefold to 128,050,070 GWh / year.

したがって、 本発明による水力発電方法を世界標準 ( def act standard 事実上の標準) として世界中に普及させれば、 地球規模 のエネルギーと環境問題が一挙に解決し、 持続可能な発展社会が実 現できる。  Therefore, if the hydroelectric power generation method according to the present invention is spread around the world as a global standard (def act standard), global energy and environmental problems will be solved at once, and a sustainable development society will be realized. it can.

( 1 5 ) 本発明は、 I S 0 1 4 0 0 0シリーズのライフサイクル - アセスメン トから最高の評価を受けるだろう。 それは、 本発明の水 力発電は、 ダム湖の電力調節、 洪水防御、 利水、 砂防、 魚道確保な どの機能を永久的に維持し、 取水管、 導水管、 排砂管の耐用年数は 永久的であり、 永遠に発電し続け、 持続可能な発展社会を実現する からである。 ライフサイクル '.アセスメン トとは、 原料採取から廃 棄に至るまでの製品のライフサイクル全般にわたつて環境への負荷 を減らしていく手法を追及するための規格である。 この手法を用い て各種の発電ブラン 卜の建てるために費やしたエネルギーとそのプ ラン 卜を運転するために必要なエネルギーの合計を投入エネルギー とする。 それに対して発電プラン 卜を稼働して得られた産出エネル ギ—の総量を投入エネルギーで割った値 (産出エネルギ) / (投入 エネルギー) を求める。 在来方法で最も (産出エネルギ) / (投入 エネルギー) の値が高いのは中小水力で 4 0倍である。 最も低いの は太陽光発電で 3倍である。 (15) The present invention will receive the highest rating from the IS01400 series life cycle-assessment. That is, the hydroelectric power generation of the present invention can permanently maintain functions such as power regulation of dam lakes, flood protection, water use, sabo control, and securing of fish passages, and the service life of intake pipes, conduits, and sand discharge pipes It is permanent, generates electricity forever, and realizes a sustainable development society. Life cycle '. Assessment is a standard for pursuing methods to reduce the burden on the environment throughout the product life cycle from raw material extraction to disposal. The total energy consumed to build various power plants and the energy required to operate the plant using this method is taken as the input energy. On the other hand, the value (output energy) / (input energy) is obtained by dividing the total amount of output energy obtained by operating the power plant by the input energy. The highest value of (output energy) / (input energy) in the conventional method is 40 times for small and medium-sized hydropower. The lowest is solar power tripled.

これは耐用年数が 2 0年と短く、 生産時にエネルギーを大量に使 い、 その量は太陽光発電量の 6年分相当だからである。 石油火力発 電は 2 0倍強、 原子力発電と石炭火力発電は 1 7倍、 地熱発電は 2 0倍、 風力発電は 1 0倍である。 本発明の水力発電は、 同一地点、 同一規模の在来中小水力発電の数十倍の発電し、 耐用年数は永久的 で、 リサイクルのエネルギー消費はゼロであり、 (産出エネルギ) / (投入エネルギー) の値は何千倍にもなる。  This is because the service life is as short as 20 years, a large amount of energy is used during production, and that amount is equivalent to six years of solar power generation. Oil-fired power is slightly more than 20 times, nuclear power and coal-fired power are 17 times, geothermal is 20 times and wind power is 10 times. The hydroelectric power generation of the present invention generates several tens of times the size of conventional small and medium-sized hydroelectric power generation at the same location and the same scale, has a permanent service life, has no recycling energy consumption, and (output energy) / (input energy). ) Can be thousands of times.

産業上の利用可能性 Industrial applicability

以上説明したように、 本発明の水力発電方法は、 膨大なエネルギ 一を使わずに、 水力発電をしながら砂礫を平野部まで流送でき、 か つ、 ダム本来の機能である水力発電、 揚水発電、 洪水防御、 利水、 砂防、 魚道確保等を永久に維持できるので、 自然環境に優しく安全 で経済的にも著しく有利である。  As described above, the hydroelectric power generation method of the present invention can transfer gravel to plains while generating hydroelectric power without using a huge amount of energy. Since power generation, flood protection, water use, sabo control, fishway access, etc. can be maintained forever, it is environmentally friendly, safe and economically advantageous.

Claims

請求の範囲 The scope of the claims 1 . ダム湖の湖底にダム堰堤から上流部に延びる取水管を設ける と共に、 その先端に取水口を設け、 さらに取水管の途中にもダム湖 の湖底に沿って複数個の枝管を配設すると共に、 その先端に取水口 を設け、 一方、 前記取水管に排水弁を介して通じていると共に、 ダ 厶堰堤の下流側に導出されて発電所の水車に通じている導水管を設 け、 水力発電時には、 導水管から発電所の水車に水を供給して発電 すると共に、 ダム湖に流下する土砂や有機物を取水管および枝管の 取水口から吸引して排出するような水力発電方法において、 1. At the bottom of the dam lake, an intake pipe extending from the dam dam to the upstream, an intake port at the tip, and a plurality of branch pipes along the bottom of the dam lake along the intake pipe At the same time, an intake port is provided at the end of the pipe, and a water pipe is connected to the intake pipe via a drain valve and is connected to the water turbine of the power plant that is led out downstream of the dam dam. At the time of hydroelectric power generation, water is supplied from a water pipe to a turbine of a power plant to generate electricity, and at the same time, sediment and organic substances flowing down to a dam lake are sucked and discharged from intakes of water pipes and branch pipes. At 前記取水管を可撓性を有する管継手を介して接続された複数の配 管から構成して、 各配管の先端の取水口を湖底の隅々まで移動可能 にすると共に、 各配管の内面を軟質ゴム製のチュ一プの外周面に着 色ウレタンゴム層を設けてなるライニングチューブでライニングし. 軟質ゴムが摩耗してゥ レタンゴム層が露出したらライニングの取替 え準備を してライニングだけを取替えて、 取水管の耐用年数を永久 化することを特徴とする水力発電方法。  The water intake pipe is composed of a plurality of pipes connected via flexible pipe joints, and the water intake at the tip of each pipe can be moved to every corner of the lake bottom, and the inner surface of each pipe is formed. Lining with a lining tube provided with a colored urethane rubber layer on the outer peripheral surface of a soft rubber tube. When the soft rubber wears out and the urethane rubber layer is exposed, prepare the lining for replacement and use only the lining. A hydroelectric power generation method characterized by making the service life of an intake pipe permanent by replacing it. 2 . ダム堰堤の下流側に集魚プールを設けると共に、 その集魚プ —ルからダム湖に通じる潜孔魚道を設け、 ダム湖の貯水を水力発電 に使う場合は、 その水位が回遊魚が上流に溯上可能な水位 H 1 以上 に達した際には、 ダム湖の貯水を前記排水弁を開いて導水管に流し、 その水位が前記集魚プールまで溯上して来た魚が潜孔魚道を通って 溯上可能な水位差 Δ hになるような水位 H 2になるまで使いきると 同時に、 潜孔魚道の水門を開いて、 集魚プールの魚を溯上させ、 水 位差△ hがゼロになった時、 潜孔魚道の水門を閉じるようにしたこ とを特徴とする請求の範囲第 1項に記載の水力発電方法。  2. A fish collection pool will be provided downstream of the dam dam, and a submerged fish passage will be established from the fish collection pool to the dam lake. If the reservoir of the dam lake is used for hydroelectric power generation, the water level will be higher than the migratory fish. When the water level at which the water can reach the upstream reaches H1 or higher, the drainage reservoir is opened and the drainage valve is opened to drain the water into the water collection pipe. As soon as the water level H2 is used up so that the water level difference Δh can be reached, the sluice of the cave fishway is opened, and the fish in the fish collection pool are advanced, and the water level difference △ h becomes zero. 2. The hydroelectric power generation method according to claim 1, wherein the sluice gate of the submerged fishway is closed when the spillage occurs. 3 . ダム湖の上流に巨礫流下防止堰堤を造り、 その堰堤は、 粒径 が所定値以下の砂礫および水をダム湖に流し、 粒径が所定値を超え た巨礫や流木や木の枝は、 そこで塞き止められるような縦長の切り 目を有する構造とし、 さらに、 前記巨礫流下防止堰堤の上流側に集 魚プールを設けると共に、 下流側にもダム湖に通じる他の集魚プ— ルを設け、 また上流側集魚プールと巨礫流下防止堰堤との間および ダム湖と前記他の集魚プールとの間に、 それそれ複数個の潜孔魚道 とその水門を設けて、 その水門を適時開閉することによって魚が上 流と下流の両方向に行き来できるようにしたことを特徴とする請求 の範囲第 1項に記載の水力発電方法。 3. A boulder flow prevention dam will be constructed upstream of the dam lake, and the dam will flow gravel and water with a particle size below a specified value to the dam lake, and the particle size will exceed the specified value. The boulders, driftwood, and tree branches have vertical cuts that can be blocked there.Furthermore, a fish pool is provided upstream of the boulder flow prevention dam, and a dam lake is also provided downstream. There are also other fish collection pools leading to the river, and between the upstream fish collection pool and the boulder flow prevention dam and between the dam lake and the other fish collection pool, there are a plurality of cave fishways and their locks. 2. The hydroelectric power generation method according to claim 1, wherein a fishgate is provided so as to be able to move in both upstream and downstream directions by opening and closing the lock as appropriate. 4 . 導水管と発電所との間に砂礫分離槽 1 1 を配設すると共に、 導水管の延長線上には砂礫分離槽 1 1 で分離された砂礫.を排出する ための排砂管を配設し、 取水管に吸引された水、 砂礫および有機物 を、 前記排水弁を開いて導水管を介して排出し、 さらに砂礫分離槽 1 1 において水および有機物と砂礫とに分離し、 水および有機物を 発電所の水車を経由して河川に放流すると共に、 砂礫を排砂管を介 して砂礫集積所まで流送することを特徴とする請求の範囲第 1 項に 記載の水力発電方法。  4. A gravel separation tank 11 will be installed between the headrace and the power plant, and a sand drainage pipe for discharging the gravel separated in the gravel separation tank 11 will be provided on the extension of the headrace. The drainage valve is opened to discharge the water, gravel and organic matter sucked into the intake pipe through the water pipe, and further separated into water, organic matter and gravel in the gravel separation tank 1 1, The hydroelectric power generation method according to claim 1, wherein the water is discharged into a river via a turbine of a power plant, and the gravel is transported to a gravel accumulation point via a sand drain pipe.
PCT/JP2002/005476 2001-06-04 2002-06-04 Hydroelectric power generating method Ceased WO2002099202A1 (en)

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WO2007095680A1 (en) * 2006-02-24 2007-08-30 Jozef Goj System to propel fluid matter in an elongate flow tube
CN101275392B (en) * 2007-03-30 2011-04-27 曾兆仁 Method for preventing water loss and soil erosion and method for building non-leakage water reservoir
CN101525875B (en) * 2009-04-07 2011-08-17 中国水电顾问集团华东勘测设计研究院 Reinforced concrete bifurcated pipe structure under action of high pressure water and construction method
WO2013024992A3 (en) * 2011-08-12 2013-04-11 (주)써포텍 Apparatus for removing sediment from water intake path or water discharge path of plant
CN103397620A (en) * 2013-05-20 2013-11-20 侯献贵 Water saving type hydropower station
JP2014173252A (en) * 2013-03-06 2014-09-22 Hiroshi Ito Efficient deposition sediment movement system to water reservoir dead water region
CN104480916A (en) * 2014-12-13 2015-04-01 中国电建集团贵阳勘测设计研究院有限公司 Method for sub-assembly of high-flow mixed hydropower station
WO2017184005A1 (en) * 2016-04-21 2017-10-26 Tesla Tomislav Vacuuming sediment from river reservoirs
JP2022541956A (en) * 2020-05-27 2022-09-28 中国長江三峡集団有限公司 Ecological regulation of mainstream reservoirs considering inflow from regional tributaries

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JPH05179631A (en) * 1991-12-27 1993-07-20 Hazama Gumi Ltd Dam structure
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007095680A1 (en) * 2006-02-24 2007-08-30 Jozef Goj System to propel fluid matter in an elongate flow tube
CN101275392B (en) * 2007-03-30 2011-04-27 曾兆仁 Method for preventing water loss and soil erosion and method for building non-leakage water reservoir
CN101525875B (en) * 2009-04-07 2011-08-17 中国水电顾问集团华东勘测设计研究院 Reinforced concrete bifurcated pipe structure under action of high pressure water and construction method
WO2013024992A3 (en) * 2011-08-12 2013-04-11 (주)써포텍 Apparatus for removing sediment from water intake path or water discharge path of plant
JP2014173252A (en) * 2013-03-06 2014-09-22 Hiroshi Ito Efficient deposition sediment movement system to water reservoir dead water region
CN103397620A (en) * 2013-05-20 2013-11-20 侯献贵 Water saving type hydropower station
CN104480916A (en) * 2014-12-13 2015-04-01 中国电建集团贵阳勘测设计研究院有限公司 Method for sub-assembly of high-flow mixed hydropower station
WO2017184005A1 (en) * 2016-04-21 2017-10-26 Tesla Tomislav Vacuuming sediment from river reservoirs
JP2022541956A (en) * 2020-05-27 2022-09-28 中国長江三峡集団有限公司 Ecological regulation of mainstream reservoirs considering inflow from regional tributaries
JP7232451B2 (en) 2020-05-27 2023-03-03 中国長江三峡集団有限公司 Ecological regulation of mainstream reservoirs considering inflow from regional tributaries

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