TW202012040A - Water supply device and water supply method - Google Patents
Water supply device and water supply method Download PDFInfo
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- TW202012040A TW202012040A TW108114374A TW108114374A TW202012040A TW 202012040 A TW202012040 A TW 202012040A TW 108114374 A TW108114374 A TW 108114374A TW 108114374 A TW108114374 A TW 108114374A TW 202012040 A TW202012040 A TW 202012040A
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J4/00—Feed or outlet devices; Feed or outlet control devices
- B01J4/04—Feed or outlet devices; Feed or outlet control devices using osmotic pressure using membranes, porous plates
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F03—MACHINES OR ENGINES FOR LIQUIDS; WIND, SPRING, OR WEIGHT MOTORS; PRODUCING MECHANICAL POWER OR A REACTIVE PROPULSIVE THRUST, NOT OTHERWISE PROVIDED FOR
- F03G—SPRING, WEIGHT, INERTIA OR LIKE MOTORS; MECHANICAL-POWER PRODUCING DEVICES OR MECHANISMS, NOT OTHERWISE PROVIDED FOR OR USING ENERGY SOURCES NOT OTHERWISE PROVIDED FOR
- F03G7/00—Mechanical-power-producing mechanisms, not otherwise provided for or using energy sources not otherwise provided for
- F03G7/04—Mechanical-power-producing mechanisms, not otherwise provided for or using energy sources not otherwise provided for using pressure differences or thermal differences occurring in nature
- F03G7/05—Ocean thermal energy conversion, i.e. OTEC
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F04—POSITIVE - DISPLACEMENT MACHINES FOR LIQUIDS; PUMPS FOR LIQUIDS OR ELASTIC FLUIDS
- F04D—NON-POSITIVE-DISPLACEMENT PUMPS
- F04D33/00—Non-positive-displacement pumps with other than pure rotation, e.g. of oscillating type
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- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
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Abstract
Description
本發明係關於一種供水裝置及供水方法。更具體而言,係關於一種不使用電動機等動力,即可供水之供水裝置及供水方法。 The invention relates to a water supply device and a water supply method. More specifically, it relates to a water supply device and a water supply method that can supply water without using power such as an electric motor.
近年來,為阻止全球沙漠化發展,已嘗試在世界各地之沙漠地區及乾燥地區種植植物綠化。然而,沙漠地區及乾燥地區,多位於遠離大型河川等水源之地區,在沙漠綠化方面,確保植物所需水源成為重要之課題。在遠離河川等水源之地區,透過挖掘水井、透過泵浦等設備抽取地下水來確保水源。為了沙漠綠化,必須連續且穩定地供給植物大量水。在泵浦方面,亦因需使用柴油機、電動機、燃氣輪機等做為動力源,更需要大量燃料或電力來驅動諸等動力源。卻由於沙漠地區及乾燥地區多處於邊鄙之地,運作泵浦動力源所需燃料或電力之運輸成本,便成為綠化之障礙。 In recent years, in order to prevent the development of global desertification, attempts have been made to plant plants in desert areas and dry areas around the world. However, desert areas and dry areas are mostly located in areas far away from large rivers and other water sources. In the area of desert greening, ensuring the water sources required by plants has become an important issue. In areas far away from water sources such as rivers and rivers, water sources are secured by digging wells and pumping groundwater through equipment such as pumps. For desert greening, plants must be continuously and stably supplied with large amounts of water. In terms of pumping, because of the need to use diesel engines, electric motors, gas turbines, etc. as power sources, it also requires a large amount of fuel or electricity to drive various power sources. However, because desert areas and dry areas are mostly in marginal areas, the transportation cost of fuel or electricity required to operate the pump power source has become an obstacle to greening.
傳統上,為供應泵浦運作所需電力,考慮過導入風力發電及太陽能發電,卻因設備等建設成本及發電效率等觀點而遲遲無法導入。在沙漠地區或乾燥地區進行綠化時,冀望有不使用燃料及電力而汲取地下水之泵浦。 Traditionally, the introduction of wind power and solar power has been considered for the supply of power required for pumping operations, but it has been delayed due to the construction cost of equipment and power generation efficiency. When carrying out greening in desert or dry areas, we hope to have a pump that draws groundwater without using fuel and electricity.
作為不使用燃料或電力進行驅動之泵浦,提出了利用半透膜使液體移動,亦即利用滲透壓現象之滲透壓泵浦(專利文獻1、專利文獻2)。 As a pump driven without using fuel or electricity, an osmotic pump that uses a semi-permeable membrane to move liquid, that is, an osmotic pressure phenomenon has been proposed (
此外,將氧化鋁粒子之高填充泥漿作為多孔質層使用,使這 些多孔質層浸泡於液體中,提出了在多孔質層之第一表面側之液體層與第二表面側之液體層之間產生壓力差之抽水裝置(專利文獻3)。 In addition, using a highly filled slurry of alumina particles as the porous layer and immersing these porous layers in the liquid, it has been proposed between the liquid layer on the first surface side and the liquid layer on the second surface side of the porous layer Pumping device that produces a pressure difference (Patent Document 3).
[先前技術文獻] [Prior Technical Literature]
專利文獻 Patent Literature
專利文獻1:日本專利特開2009-115755號公報 Patent Document 1: Japanese Patent Laid-Open No. 2009-115755
專利文獻2:日本專利特開2010-25067號公報 Patent Document 2: Japanese Patent Laid-Open No. 2010-25067
專利文獻3:日本專利特開2005-233094號公報 Patent Document 3: Japanese Patent Laid-Open No. 2005-233094
然而,專利文獻1、2所述之技術,係將半透膜隔開之二個液室內之溶液濃度差所造成之滲透壓作為驅動力使用之技術。這種滲透壓泵浦,需要兩個液室之間有經常性的溶液濃度差異,並且需費時調整各液室間之濃度。此外,二個液室間之溶液濃度差一旦穩定下來,便不會發生滲透壓,因此很難長時間不間斷地使用。甚至,這些技術係使用形成於基板上、被稱為微管道(microchannel)之微細流路或通口等細微結構中控制流體之送液手段,存在著送液量微小之問題。 However, the technology described in
此外,專利文獻3所述技術,由於抽水原理不明,而難以應用開發,此外,還存在著難以提升裝置能力之問題。 In addition, the technology described in
鑒於如上傳統技術之問題點,本發明之目的,即是提供一種供水裝置及供水方法,即便不使用燃料或電力做為所需動力源,亦可供水,此外,亦可增加供水量,甚至,亦可增加揚程。 In view of the above problems of the conventional technology, the object of the present invention is to provide a water supply device and a water supply method, which can supply water even without using fuel or electricity as a required power source. In addition, the water supply can be increased, and even, It can also increase the head.
此外,本發明之目的,在於提供一種供水裝置及供水方法,毋需透過半透膜來調整相鄰之各水層之濃度或確保負壓等繁雜操作,此外,可長期不間斷性使用。 In addition, the object of the present invention is to provide a water supply device and a water supply method, which does not require complicated operations such as adjusting the concentration of adjacent water layers or ensuring negative pressure through a semi-permeable membrane, and can be used continuously for a long time.
本發明者等經潛心研究結果,發現可利用存在於粒子表面之電雙層重疊效應所產生之滲透壓來進行供水。根據本發明,提供一種如下所示之供水裝置及供水方法。 The inventors of the present invention have made painstaking research and found that the osmotic pressure generated by the electric double layer overlapping effect existing on the surface of the particles can be used for water supply. According to the present invention, there is provided a water supply device and a water supply method as shown below.
[1]一種供水裝置,其中具備多個筒狀之單元。該各單元,除下端設有半透膜,並以垂直方向堆疊之狀態相互連通外,且容納有水中分散著粒子之懸浮水;該半透膜配置為將該懸浮水與配設有該半透膜之單元下側相鄰之水隔開;該懸浮水中之粒子沉降於該半透膜上,形成堆積層,在該堆積層中,因形成於該粒子表面之電雙層重疊效應而產生滲透壓,並以該滲透壓作為驅動源,透過該半透膜從相鄰之水進行供水。 [1] A water supply device including a plurality of cylindrical units. The units are provided with a semi-permeable membrane at the lower end and are connected to each other in a vertically stacked state, and contain suspended water in which particles are dispersed in the water; the semi-permeable membrane is configured to configure the suspended water and the semi-permeable membrane The water below the unit of the permeable membrane is separated by adjacent water; the particles in the suspended water settle on the semi-permeable membrane to form a build-up layer, which is caused by the electric double layer overlapping effect formed on the surface of the particles Osmotic pressure, and use the osmotic pressure as the driving source to supply water from the adjacent water through the semi-permeable membrane.
[2]一種供水裝置,其中具備多個筒狀之單元。該各單元,除下端設有半透膜,並以垂直方向堆疊之狀態相互連通外,且容納有水中分散著粒子之懸浮水;該懸浮水之水面與該單元之內壁之間形成一空間,於該空間內,在較該水面靠上側之位置設置有通氣孔;該半透膜配置為將該懸浮水與配設有該半透膜之單元下側相鄰之水隔開;該懸浮水中之粒子沉降於該半透膜上,形成堆積層,在該堆積層中,因形成於該粒子表面之電雙層重疊效應而產生滲透壓,並以該滲透壓作為驅動源,透過該半透膜從相鄰之水進行供水。 [2] A water supply device including a plurality of cylindrical units. The units are provided with a semi-permeable membrane at the lower end and are connected to each other in a vertically stacked state, and contain suspended water in which particles are dispersed in the water; a space is formed between the surface of the suspended water and the inner wall of the unit In the space, a vent hole is provided on the upper side of the water surface; the semi-permeable membrane is configured to separate the suspended water from the water adjacent to the lower side of the unit equipped with the semi-permeable membrane; the suspension The particles in the water settle on the semi-permeable membrane to form a build-up layer. In the build-up layer, the osmotic pressure is generated due to the electric double layer overlapping effect formed on the surface of the particles, and the osmotic pressure is used as the driving source to pass through the semi-permeable layer. The permeable membrane supplies water from the adjacent water.
[3]如第[1]或[2]項所述之供水裝置,其中在該單元內,該懸浮水中之粒子沈降,形成該粒子堆積之堆積層,以及與該堆積層上側相鄰,且實質上不包含該粒子之澄清層。 [3] The water supply device according to item [1] or [2], wherein in the unit, particles in the suspended water settle to form a buildup layer in which the particles accumulate and are adjacent to the upper side of the buildup layer, and The clear layer does not substantially contain the particles.
[4]如第[3]項所述之供水裝置,其中在該單元內,實質上不包含該粒子之該澄清層液面與該單元內壁之間形成空間。 [4] The water supply device according to item [3], wherein in the unit, a space is formed between the liquid surface of the clear layer that does not substantially contain the particles and the inner wall of the unit.
[5]如第[4]項所述之供水裝置,其中在該單元內,實質上不 包含該粒子之該澄清層液面與該單元內壁之間所形成之空間壓力為大氣壓。 [5] The water supply device according to item [4], wherein the pressure of the space formed between the liquid surface of the clarified layer that does not substantially contain the particles and the inner wall of the unit in the unit is atmospheric pressure.
[6]如第[1]~[5]項之任一項所述之供水裝置,其中該粒子係在水中形成電雙層之粒子。 [6] The water supply device according to any one of items [1] to [5], wherein the particles are particles that form an electric double layer in water.
[7]如第[1]~[6]項之任一項所述之供水裝置,其中該粒子係金屬氧化物。 [7] The water supply device according to any one of items [1] to [6], wherein the particles are metal oxides.
[8]一種供水方法,其具備以下步驟:於水中填充有粒子分散之懸浮水,將下端設有半透膜之單元沿垂直方向堆積;使位於最底部之單元之半透膜與該單元下端相鄰之水接觸;以及藉由沈降堆積於該各單元內之該半透膜上之該粒子之電雙層重疊效應,所產生之滲透壓作為驅動源,再從該各單元下端相鄰之水透過半透膜向上方進行供水。 [8] A water supply method, comprising the steps of: filling suspended water with dispersed particles in water, stacking the unit with a semi-permeable membrane at the lower end in a vertical direction; making the semi-permeable membrane of the unit at the bottom and the lower end of the unit Adjacent water contact; and by the double layer overlapping effect of the particles deposited on the semi-permeable membrane in each unit, the generated osmotic pressure is used as a driving source, and then from the lower end of each unit The water is supplied upward through the semi-permeable membrane.
[9]如第[8]項所述之供水方法,其中於各單元內,該懸浮水中之粒子沈降,形成該粒子堆積之堆積層,以及與該堆積層上側相鄰且實質上不包含該粒子之澄清層。 [9] The water supply method according to item [8], wherein in each unit, particles in the suspended water settle to form a buildup layer in which the particles accumulate, and the upper side of the buildup layer adjacent to and substantially excluding the A clear layer of particles.
[10]如第[9]項所述之供水方法,其中在該單元內,實質上不包含該粒子之該澄清層液面與該單元內壁之間形成空間。 [10] The water supply method according to item [9], wherein in the unit, a space is formed between the liquid surface of the clear layer that does not substantially contain the particles and the inner wall of the unit.
[11]如第[10]項所述之供水方法,其中在該單元內,實質上不包含該粒子之該澄清層液面與該單元內壁之間所形成之空間壓力為大氣壓。 [11] The water supply method according to item [10], wherein the pressure of the space formed between the liquid surface of the clarified layer that does not substantially contain the particles and the inner wall of the unit in the unit is atmospheric pressure.
[12]如第[8]~[11]項之任一項所述之供水方法,其中該粒子為在水中形成電雙層之粒子。 [12] The water supply method according to any one of items [8] to [11], wherein the particles are particles that form an electric double layer in water.
[13]如第[8]~[12]項之任一項所述之供水方法,其中該粒子 為金屬氧化物。 [13] The water supply method according to any one of items [8] to [12], wherein the particles are metal oxides.
根據本發明之供水裝置,即便不使用燃料或電力做為所需動力源,亦可供水,此外,具可增加供水量及揚程之效果。此外,根據本發明之供水裝置,毋需透過半透膜來調整相鄰之各水層之濃度等繁雜操作,此外,可達長期不間斷性使用之效果。 According to the water supply device of the present invention, water can be supplied even without using fuel or electricity as a required power source. In addition, it has the effect of increasing the water supply amount and head. In addition, according to the water supply device of the present invention, there is no need for complicated operations such as adjusting the concentration of adjacent water layers through a semi-permeable membrane, and in addition, the effect of long-term uninterrupted use can be achieved.
1‧‧‧粒子 1‧‧‧ particles
2‧‧‧電雙層 2‧‧‧Electric double layer
3‧‧‧半透膜 3‧‧‧ Semi-permeable membrane
10‧‧‧供水裝置 10‧‧‧Water supply device
11‧‧‧傳輸管 11‧‧‧Transmission tube
12‧‧‧半透膜 12‧‧‧ Semi-permeable membrane
13‧‧‧單元 13‧‧‧ unit
14‧‧‧水 14‧‧‧ water
15‧‧‧堆積層 15‧‧‧Stacked layer
16‧‧‧泥漿層 16‧‧‧Mud layer
17‧‧‧澄清層 17‧‧‧Clarification layer
20‧‧‧單元 20‧‧‧ unit
21‧‧‧吸水口 21‧‧‧Suction port
22‧‧‧半透膜 22‧‧‧ Semi-permeable membrane
23‧‧‧通氣孔 23‧‧‧ vent
24‧‧‧容器 24‧‧‧Container
25‧‧‧堆積層 25‧‧‧Stacked layer
26‧‧‧澄清層 26‧‧‧Clarification layer
27‧‧‧空間 27‧‧‧Space
28‧‧‧流出口 28‧‧‧ Outflow
30‧‧‧供水裝置 30‧‧‧Water supply device
40‧‧‧吸水裝置 40‧‧‧Water absorption device
41‧‧‧單元 41‧‧‧ unit
42‧‧‧泥漿 42‧‧‧Mud
43‧‧‧膜濾網 43‧‧‧membrane filter
44‧‧‧離子交換水 44‧‧‧Ion exchanged water
45‧‧‧儲水槽 45‧‧‧Water storage tank
46‧‧‧凸部 46‧‧‧Convex
71‧‧‧傳輸管 71‧‧‧Transmission tube
72‧‧‧沈降管 72‧‧‧settler
73‧‧‧膜濾網 73‧‧‧membrane filter
74‧‧‧儲水槽 74‧‧‧Water storage tank
75‧‧‧連結管 75‧‧‧Connecting tube
76‧‧‧堆積層 76‧‧‧Stacked layer
77‧‧‧泥漿層 77‧‧‧ Mud layer
78‧‧‧澄清層 78‧‧‧Clarification layer
79‧‧‧蒸餾水 79‧‧‧ distilled water
A‧‧‧電雙層重疊領域 A‧‧‧Electronic double-layer overlapping field
B‧‧‧斥力 B‧‧‧Repulsion
C‧‧‧儲水容器 C‧‧‧Water storage container
D‧‧‧連結管 D‧‧‧Connecting tube
h‧‧‧投入高度 h‧‧‧ input height
△h0‧‧‧初期水位差 △h 0 ‧‧‧ Initial water level difference
圖1係表示分散於水中之粒子間之靜電相互作用如何產生斥力之示意圖。 FIG. 1 is a schematic diagram showing how electrostatic interaction between particles dispersed in water generates a repulsive force.
圖2係用於說明如何利用粒子堆積於半透膜上形成堆積層產生供水機制之示意圖。 FIG. 2 is a schematic diagram illustrating how a particle is deposited on a semi-permeable membrane to form a build-up layer to generate a water supply mechanism.
圖3係示意性地表示本發明之供水裝置之一實施方式之截面圖。 3 is a cross-sectional view schematically showing an embodiment of the water supply device of the present invention.
圖4係表示單元內之懸浮水狀態之示意圖。 Figure 4 is a schematic diagram showing the state of suspended water in the unit.
圖5係示意性地表示本發明之供水裝置之其他實施方式中使用之單元之截面圖。 5 is a cross-sectional view schematically showing a unit used in another embodiment of the water supply device of the present invention.
圖6係示意性地表示本發明之供水裝置之其他實施方式之截面圖。 6 is a cross-sectional view schematically showing another embodiment of the water supply device of the present invention.
圖7係示意性地表示用於供水機制之確認實驗之實驗裝置之截面圖。 FIG. 7 is a cross-sectional view schematically showing an experimental device used for the confirmation experiment of the water supply mechanism.
圖8係泥漿之pH值與靜水壓之關係圖。 Figure 8 is a graph of the relationship between the pH of the mud and the hydrostatic pressure.
圖9係泥漿之pH值與氧化鋁粒子之位能之關係圖。 Fig. 9 is a graph showing the relationship between the pH value of mud and the potential energy of alumina particles.
圖10係時間與靜水壓之關係及時間與吸水速度之關係圖。 Figure 10 is the relationship between time and hydrostatic pressure and the relationship between time and water absorption rate.
圖11係時間與平移能之關係及時間與累積吸水量之關係圖。 Figure 11 is the relationship between time and translational energy and the relationship between time and cumulative water absorption.
圖12係用於性能評價之供水裝置之照片。 Figure 12 is a photograph of a water supply device used for performance evaluation.
圖13係時間與靜水壓之關係圖。 Figure 13 is the relationship between time and hydrostatic pressure.
圖14係水位差為19cm時,累積吸水量與時間之關係圖。 Figure 14 shows the relationship between cumulative water absorption and time when the water level difference is 19cm.
圖15係示意性地表示用於粒子帶電符號之影響確認實驗之吸水裝置之截面圖。 Fig. 15 is a cross-sectional view schematically showing a water-absorbing device used for the confirmation experiment of the influence of the charged symbol of particles.
圖16係時間與累積吸水量之關係圖。 Figure 16 shows the relationship between time and cumulative water absorption.
圖17係時間與累積吸水量之關係圖。 Figure 17 shows the relationship between time and cumulative water absorption.
圖18係時間與累積吸水量之關係圖。 Figure 18 is the relationship between time and cumulative water absorption.
圖19係時間與累積吸水量之關係圖。 Figure 19 is the relationship between time and cumulative water absorption.
以下說明本發明之實施方式,唯應理解本發明並不限定於以下實施方式。即,本發明所屬技術領域中具有通常知識者可在不背離本發明之趣旨範圍內,對以下實施方式進行適當變更及修改,而仍屬於本發明之範圍。 The following describes the embodiments of the present invention, but it should be understood that the present invention is not limited to the following embodiments. That is, those with ordinary knowledge in the technical field to which the present invention belongs can make appropriate changes and modifications to the following embodiments without departing from the scope of the present invention, and still fall within the scope of the present invention.
(1)供水機制 (1) Water supply mechanism
在說明本發明之實施方式之供水裝置前,先對供水機制進行說明。在本實施方式之供水裝置中,原本粒子分散於水中之懸浮水中之粒子沈降,形成堆積層。接著,將粒子堆積而成之堆積層產生之滲透壓作為供水之驅動源。在此,首先對存在於粒子表面之電雙層如何產生滲透壓進行說明。圖1係顯示分散於水中之粒子間之靜電相互作用如何產生斥力之示意圖。分散於水中之粒子表面,因解離基或吸附離子等因素而帶電。與粒子表面電荷帶相反符號電荷之電解質離子(以下稱”相對離子“)在粒子表面附近形成層狀分佈。這種相對離子之分佈層稱為“電雙層”。這種電雙層,分為固定層(無圖示)與擴散層等兩部分。所謂固定層,係指相對離子透過與粒子表面之引力被強烈固定之部分。所謂擴散層,係指透過熱運動產生的離子擴散現象,使相對離子濃度緩慢減少之部分。如圖1所示,具備電雙層2之粒子1彼此互相接近時,每個粒子1所具有的電雙層2就會重疊。電雙 層2重疊領域A較周圍的相對離子濃度更高,便會產生液體傾向進入該重疊效應領域A之壓力(滲透壓)。而斥力B憑藉該壓力(滲透壓)作用於粒子1之間。 Before describing the water supply device according to the embodiment of the present invention, the water supply mechanism will be described. In the water supply device of this embodiment, the particles in the suspended water in which the particles were originally dispersed in the water settle down to form a buildup layer. Next, the osmotic pressure generated by the accumulation layer formed by the particles is used as the driving source of the water supply. Here, first, how the electric double layer existing on the particle surface generates osmotic pressure will be described. FIG. 1 is a schematic diagram showing how electrostatic interaction between particles dispersed in water generates a repulsive force. The surface of particles dispersed in water is charged due to factors such as dissociation groups or adsorbed ions. Electrolyte ions (hereinafter referred to as "relative ions") with a charge opposite to the particle surface charge form a layered distribution near the particle surface. This distribution of relative ions is called "electric double layer". This electrical double layer is divided into a fixed layer (not shown) and a diffusion layer. The so-called fixed layer refers to the part where the relative ion penetration and the gravity of the particle surface are strongly fixed. The so-called diffusion layer refers to the part of the ion diffusion phenomenon caused by thermal motion, which slowly reduces the relative ion concentration. As shown in FIG. 1, when the
本實施方式之供水裝置,推論為透過滲透壓產生之斥力作用來進行供水。並認為,如此透過滲透壓產生之斥力作用所進行之供水,乃透過圖2所示之機制進行。圖2係用於說明如何利用粒子堆積於半透膜上形成堆積層產生供水機制之示意圖。如圖2所示,電雙層2存在於各粒子1之表面,粒子1沈降於無法使粒子1通過的半透膜3,並堆積形成堆積層。在堆積層內,粒子1之間的電雙層2相互重疊。在堆積層下部,由於粒子1被緊密壓縮,故粒子1不動。相較於堆積層下部,粒子1在堆積層上部更可移動。於該堆積層中,粒子1之間的電雙層2相互重疊,產生滲透壓引發斥力。在此,粒子1之間的電雙層2相互重疊之區域一旦被水侵入,就會因膨潤現象而膨脹,使得電雙層2之相互重疊情況減少而使滲透壓下降。然而,卻因半透膜3妨礙了粒子1向下膨潤而膨脹,粒子1只能向上膨脹,由於該膨脹現象,如箭頭所示,產生水往上的上升流。並且,堆積層中粒子1之有效重力,變得等於流體效力與斥力產生之互斥力之和,而形成平衡狀態(動態平衡),膨脹停止,而得以向上側持續供水。 The water supply device of this embodiment is presumed to supply water by the repulsive force generated by the osmotic pressure. And believe that the water supply through the repulsive force generated by the osmotic pressure is through the mechanism shown in Figure 2. FIG. 2 is a schematic diagram illustrating how a particle is deposited on a semi-permeable membrane to form a build-up layer to generate a water supply mechanism. As shown in FIG. 2, the electric
(2)供水裝置 (2) Water supply device
以下,使用附圖說明本發明之供水裝置之一實施方式。圖3係示意性地表示本發明之供水裝置之一實施方式之截面圖。 Hereinafter, an embodiment of the water supply device of the present invention will be described using the drawings. 3 is a cross-sectional view schematically showing an embodiment of the water supply device of the present invention.
本實施方式之供水裝置,具備多個筒狀之單元。各單元在下端設置半透膜,並以垂直方向堆疊之狀態進行連通。各單元容納有粒子分散於水中之懸浮水。設置於單元下端之半透膜,配置為隔開懸浮水,以及與設置半透膜之單元下側相鄰之水。懸浮水中之粒子沈降於半透膜上,形 成堆積層,在堆積層中,透過形成於粒子表面之電雙層重疊效應,產生滲透壓,再以該滲透壓為驅動源,透過半透膜從相鄰之水進行供水。 The water supply device of this embodiment includes a plurality of cylindrical units. Each unit is provided with a semi-permeable membrane at the lower end and communicates in a state of being stacked vertically. Each unit contains suspended water in which particles are dispersed in water. The semi-permeable membrane provided at the lower end of the unit is configured to separate suspended water and water adjacent to the lower side of the unit provided with the semi-permeable membrane. The particles in the suspended water settle on the semi-permeable membrane to form a build-up layer. In the build-up layer, the osmotic pressure is generated through the electrical double-layer overlapping effect formed on the surface of the particles, and then the osmotic pressure is used as the driving source to pass through the semi-permeable membrane. Adjacent water is used for water supply.
如圖3所示,供水裝置10具備多個筒狀之單元13。單元13為筒狀,其上端及下端皆開口。由於單元13像這樣兩端有開口,因此具有水可通過單元內部空間之中空結構。垂直相交於垂直方向之方向上之單元13之截面形狀,可列舉如圓形、橢圓、長圓、多角形等,唯不限於此。另,多角形包含:三角形、四角形、五角形、六角形等。即,單元13可以是垂直相交於垂直方向之方向上之截面形狀為圓等圓筒狀者,或是垂直相交於垂直方向之方向之截面形狀為多角形等角柱狀者。另,由供水效率之觀點看來,各個單元13,較佳為將垂直相交於垂直方向之方向上之截面形狀及截面積,全部統一為相同者。此外,各個單元13,較佳為將垂直方向之長度亦統一為相同長度。 As shown in FIG. 3, the
各個單元13,以垂直方向堆疊之狀態連通。若堆疊之單元13之個數在2以上,其個數雖無限制,唯考慮到供水之揚程等因素而適當設定。 The
在此,連通係指,將堆疊之多個筒狀之單元13串聯連接之狀態,並構成為使水能夠通過其內部空間之狀態。另,為防止與相鄰之單元13之間的偏差,單元13較佳為相互接合。可採用各種方式將這些單元13彼此接合在一起。例如,可採用下端為凸型,其上端為凹型,並將單元13之上端凹型與上側相鄰之單元13之下端凸型嵌合而固定之結構。另,將相鄰之單元13彼此接合之際,較佳為使垂直相交於垂直方向之方向上之相互的單元13之截面形狀之中心軸一致。另,在供水裝置10中,位於頂部之單元13中,亦可設置使水流出之流出口(無圖示)。單元13之材質,可列舉如丙烯酸樹脂、聚丙烯樹脂、氟樹脂等樹脂、合成橡膠、聚氨酯、 聚酯彈性體等有機材料、玻璃等無機材料、不鏽鋼等金屬,唯不限於此。 Here, communication refers to a state in which a plurality of stacked
如圖3所示的供水裝置10中,在傳輸管11上側堆積著多個筒狀之單元13。在此,傳輸管11容納有供水至單元13之水。傳輸管11藉由儲水容器C與連結管D相互連通。另,與儲水容器C之間的連通,亦可於傳輸管11底部、側面等任意位置上使用軟管等連結管D進行。此外,傳輸管11在垂直相交於垂直方向之方向上之截面形狀並無特殊限制。例如,傳輸管11在垂直相交於垂直方向之方向之截面形狀可為圓等圓筒狀或在垂直相交於垂直方向之方向之截面形狀可為多角形等角柱狀。另,較佳為使傳輸管11在垂直相交於垂直方向之方向之截面與同方向中單元13之截面形狀及截面積一致。傳輸管11之材質,可列舉如丙烯酸、聚丙烯等樹脂、合成橡膠、彈性體等有機材料、玻璃等無機材料、不鏽鋼等金屬。 In the
為防止傳輸管11與堆疊於其上側之單元13之間的偏差,較佳為將傳輸管11與單元13接合在一起。作為這種接合方式,可採用與單元13彼此接合之相同方式。此外,由防止漏水之觀點看來,單元13彼此接合之接合部分、傳輸管11與單元13接合之接合部分,較佳為適當地使用由橡膠等彈性材料形成之O型環等襯墊。 In order to prevent the deviation between the
單元13之內部,容納有粒子分散於水中之懸浮水。所謂懸浮水,係指粒子分散於其中之水。分散於水中之粒子,係可使粒子表面於水中形成電雙層之粒子。作為這種粒子,可使用金屬氧化物粒子、聚合物微粒等。作為金屬氧化物粒子,可列舉如氧化鋁粒子、TiO2粒子、ZrO2粒子等。此外,作為聚合物微粒等,可列舉如碳黑、石蠟、乳膠等。 The
在懸浮水中,分散於水中之粒子表面透過解離基及吸附離子等帶電。在本發明中,即便粒子表面帶正電,粒子表面附近也會形成電雙層,此外,即便粒子表面帶負電,粒子表面附近也會形成電雙層,任何情 況下皆可供水。作為表面帶正電之粒子,可列舉如氧化鋁粒子等,作為表面帶負電之粒子,可列舉如TiO2粒子(氧化鈦粒子)等。此外,透過使粒子吸附高分子電解質,亦可使粒子表面帶負電。作為這種高分子電解質,可列舉如多羧酸銨(PCA)等。分散水中時通常帶正電之氧化鋁粒子,亦可透過吸附多羧酸銨,使粒子表面帶負電。 In suspended water, the surface of particles dispersed in water is charged through dissociation groups and adsorbed ions. In the present invention, even if the surface of the particle is positively charged, an electric double layer will be formed near the surface of the particle, and even if the surface of the particle is negatively charged, an electric double layer will be formed near the surface of the particle, and water can be supplied in any case. Examples of particles with positively charged surfaces include alumina particles, and examples of particles with negatively charged surfaces include TiO 2 particles (titanium oxide particles). In addition, by making the particles adsorb the polymer electrolyte, the surface of the particles can also be negatively charged. Examples of such a polymer electrolyte include ammonium polycarboxylate (PCA). Alumina particles that are normally positively charged when dispersed in water can also be negatively charged by adsorbing ammonium polycarboxylate.
此外,分散於水中之粒子,以粒子表面間距離為橫軸、位能為縱軸作圖時,位能曲線具有峰值。若是位能曲線不具峰值之粒子,在粒子表面便不形成電雙層。 In addition, when the particles dispersed in water are plotted with the distance between the particle surfaces as the horizontal axis and the potential energy as the vertical axis, the potential energy curve has a peak value. In the case of particles with no potential energy curve, no electric double layer is formed on the surface of the particles.
容納於單元13之懸浮水,例如,先將在懸浮水中達到規定濃度份量之粒子添加至水中,適當混入鹽酸等分散劑後再混合。之後依規定時間使用球磨機等工具再次混合,最後透過真空脫泡得之。另,從將供水能力發揮至極限之觀點來看,懸浮水之濃度愈高愈好,可適當選擇維持粒子分散最高之濃度,並可形成足夠厚度之堆積層。 For the suspension water contained in the
單元13下端設有半透膜12。半透膜12只要具備能夠使水分子通過卻不使粒子通過之功能即可,並無特殊限制。這種半透膜12之形態,只要可進行供水,並無特殊限制。例如,可為單層膜,亦可為多層膜(複合膜)。尤其較佳為單層、平膜(片狀)。半透膜12之厚度,較佳為可確保適切強度之同時,壓力損失低且厚度較薄者。半透膜12之材質,可列舉纖維素酯等各種聚合物、紙、玻璃、陶瓷等。 A
半透膜12設置為將單元13內所容納之懸浮水與單元13下側相鄰之水隔開。即,換句話說,半透膜12設置為在單元彼此堆疊而成之單元13中,單元13內所容納之懸浮水之水層與單元13下側相鄰之單元13內所容納之懸浮水之水層之間的分界面。在供水裝置10中,懸浮水在單元13內之容納量(填充量),調整為使懸浮水之水面與該單元13上側相鄰之 單元13下端所設之半透膜12接觸。此外,半透膜12設置在單元13中最底部之單元13內所容納之懸浮水層與單元13下側相鄰之傳輸管11內容納之水層之間的分界面。懸浮水在傳輸管11內之容納量(填充量),調整為使懸浮水之水面與該傳輸管11上側相鄰之單元13下端所設置之半透膜12接觸。藉由如此設置半透膜12,使相鄰之單元13,彼此透過設置於單元13之間的半透膜12而相互連通。此外,位於單元13中最底部之單元13與傳輸管11,透過設置於單元13與傳輸管11之間的半透膜12而相互連通。另,水通過半透膜供水時,為不使半透膜12隨著水的流動而移動,具有從上側對應到單元13之截面形狀的形狀(如環狀),較佳為透過樹脂製、金屬製等半透膜按壓(無圖示)固定半透膜12之外緣。此外,單元13中容納有懸浮水,從防止懸浮水在堆疊單元13時從單元13下方流出之觀點看來,在單元13中,較佳為將半透膜12設置於多孔體上。這般多孔體,只要能妨礙懸浮水從單元13下方流出,且不阻礙水從下側流入這種程度之抵抗即可,並無特殊限制。例如,可使用Kimwipe(註冊商標)等紙、漿料形成之不織布、海綿、陶瓷、樹脂等構成之多孔體。多孔體之截面之形狀,較佳為對應單元13之截面形狀,多孔體之厚度,為了不妨礙來自下側之水流入而進行適當設定。 The
在供水裝置10中,例如,在將水填充至傳輸管11上端為止後,以使半透膜12與傳輸管11之水面接觸之方式,設置於單元13之下端。之後,將規定濃度之懸浮水填充至單元13內之上端,使到達該水面。透過如此配置半透膜12,單元13之懸浮水與填充至單元13下側相鄰之傳輸管11之水隔開。接著,以使半透膜12與單元13之懸浮水之水面接觸之方式,設置於與上側相鄰之單元13之下端,並堆疊該單元13。透過如此配置半透膜12,單元13之懸浮水與填充至單元13下側相鄰之單元13之懸浮水隔開。 另,在供水裝置10中,堆疊之單元13之數量可被稱為“段數”。例如,在傳輸管11之上側,堆疊有2個單元13時,稱為“2段之供水裝置”,在堆疊有3個單元13時,稱為“3段之供水裝置”,以下,在堆疊有N(2個以上)個單元13時,稱為“N段之供水裝置”。 In the
在供水裝置10中,單元13所容納之懸浮水中所含粒子沈降,在半透膜12上形成粒子之堆積層。以圖4說明單元13內之懸浮水之狀態。圖4係顯示單元內之懸浮水狀態之示意圖。如圖4所示,使懸浮水在水14之上側通過半透膜12填充至相鄰之單元13內上側的半透膜12並達到水面後,隨著時間流逝,懸浮水分離為粒子(無圖示)沈降於半透膜12上所堆積而成之堆積層15、粒子(無圖示)分散於水中之泥漿層16與實質上不含粒子之上清液即澄清層17等三層。另,在堆積層15中,存在於粒子表面之電雙層相互重疊。另,懸浮水中的所有粒子皆沈降,肉眼無法再辨識出泥漿層16,有時亦分離為堆積層15與澄清層17等兩層。在本實施方式之供水裝置10中,較佳為在形成粒子之堆積層之前,於單元13填充懸浮水後,依規定時間靜置單元13。靜置單元13之時間,根據粒子之種類、粒徑、懸浮水濃度、黏度等進行適當設定即可,無特殊限制。例如,單元13內粒子堆積而成之堆積層15與上清液即澄清層17分離,若能以肉眼確認以上現象,亦可判斷為形成了堆積層15。 In the
本實施方式之供水裝置10,在堆疊之多個單元13下端設置之半透膜12上形成粒子之堆積層。在形成堆積層之各單元13中,根據圖2說明之機制產生水的上升流。在堆疊之單元13中位於最底部之單元13內,與下側相鄰之傳輸管11內的水通過半透膜12上升至單元13內。上升至單元13內的水,進一步上升至與該單元13上側相鄰之單元13內。以下依序,水向更上側相鄰之單元13內上升。如此,傳輸管11內的水就會上升至堆 疊了多個單元13之供水裝置10之頂部。另,堆積層中粒子1之有效重力,變得等於流體效力與斥力產生之互斥力之和,而形成平衡狀態(動態平衡),膨潤停止,而得以向上側持續供水。 In the
(3)供水裝置 (3) Water supply device
接著,使用附圖說明本發明之供水裝置之其他實施方式。圖5係示意性地表示本發明之供水裝置之其他實施方式中使用之單元之截面圖。圖6係示意性地表示本發明之供水裝置之其他實施方式之截面圖。 Next, other embodiments of the water supply device of the present invention will be described using the drawings. 5 is a cross-sectional view schematically showing a unit used in another embodiment of the water supply device of the present invention. 6 is a cross-sectional view schematically showing another embodiment of the water supply device of the present invention.
本實施方式之供水裝置,具備多個筒狀之單元。各單元在下端設置半透膜,並以垂直方向堆疊之狀態進行連通。各單元容納有粒子分散於水中之懸浮水。懸浮水之水面與單元內壁之間形成空間,在該空間內,於水面上方設有通氣孔。此外,設置於單元下端之半透膜,配置為隔開懸浮水,以及與設置半透膜之單元下側相鄰之水。懸浮水中之粒子沈降於半透膜上,形成堆積層,在堆積層中,透過形成於粒子表面之電雙層重疊效應,產生滲透壓,再以該滲透壓為驅動源,透過半透膜從相鄰之水進行供水。 The water supply device of this embodiment includes a plurality of cylindrical units. Each unit is provided with a semi-permeable membrane at the lower end and communicates in a state of being stacked vertically. Each unit contains suspended water in which particles are dispersed in water. A space is formed between the water surface of the suspended water and the inner wall of the unit, and a vent hole is provided above the water surface in the space. In addition, the semi-permeable membrane provided at the lower end of the unit is configured to separate suspended water and water adjacent to the lower side of the unit provided with the semi-permeable membrane. The particles in the suspended water settle on the semi-permeable membrane to form a build-up layer. In the build-up layer, the osmotic pressure is generated through the electrical double-layer overlapping effect formed on the surface of the particles, and then the osmotic pressure is used as the driving source to pass through the semi-permeable membrane. Adjacent water is used for water supply.
如圖5所示,本實施方式之供水裝置中使用之單元20為筒狀,其上端及下端皆開口。由於單元20像這樣兩端有開口,因此具有水可通過單元內部空間之中空結構。垂直相交於垂直方向之方向上之單元20之截面形狀,可列舉如圓形、橢圓、長圓、多角形等,唯不限於此。另,多角形包含:三角形、四角形、五角形、六角形等。即,單元20可以是垂直相交於垂直方向之方向上之截面形狀為圓等圓筒狀者,或是垂直相交於垂直方向之方向之截面形狀為多角形等角柱狀者。此外,如圖5所示,單元20之下端側,亦可形成為開口直徑較上端開口逐漸變小之漏斗狀。另,上端附近設有通氣孔23。進而,如圖5所示,在單元20之下端,往下方向突 出設有內徑較上端之開口直徑更小之吸水口21。與吸水口21之突出方向垂直交叉方向之截面形狀,較佳為與單元20之截面形狀相同。此外,吸水口21突出方向之垂直交叉方向之截面,較佳為與同方向之單元20之上端開口之截面相互的中心軸一致。另,吸水口21設有半透膜22。作為半透膜22,可使用與上述實施方式中使用之半透膜相同者。 As shown in FIG. 5, the
如圖6所示,在本實施方式中,多個單元20以垂直方向堆疊之狀態進行連通。若堆疊之單元20之個數在2以上,其個數雖無限制,唯考慮到供水之揚程等因素而適當設定。在此,連通係指,將堆疊之多個筒狀之單元20串聯連接之狀態,並構成為使水能夠通過其內部空間之狀態。另,為防止與相鄰之單元20之間的偏差,單元20較佳為相互接合。可採用各種方式將這些單元20彼此接合在一起。例如,可採用下端為凸型,其上端為凹型,並將單元20之上端凹型與上側相鄰之單元20之下端凸型嵌合而固定之結構。另,將相鄰之單元20彼此接合之際,較佳為使垂直相交於垂直方向之方向上之相互的單元20之截面形狀之中心軸一致。另,在供水裝置30中,位於頂部之單元20中,設有使水流出之流出口28。作為單元20之材質,可使用與上述實施方式中使用之單元相同者。 As shown in FIG. 6, in this embodiment, a plurality of
單元20內部,容納著粒子分散於水中之懸浮水。作為懸浮水,可使用與上述實施方式中使用之懸浮水相同者。此外,從將供水能力發揮至極限之觀點來看,單元20內所容納之懸浮水高度(從單元底面到懸浮水液面為止之高度)愈高愈好,直到固定高度為止,可適當選擇以使吸水量達最大化。另,懸浮水在經過規定時間後,分離為堆積層25與澄清層26。在本實施方式之供水裝置30中,較佳為在形成粒子之堆積層之前,於單元20填充懸浮水後,依規定時間靜置單元20。靜置單元20之時間,根據粒子之種類、粒徑、懸浮水濃度、黏度等進行適當設定即可,無特殊限 制。 The
單元20下端之吸水口21,設有半透膜22。這種半透膜22在供水時,較佳為透過與上述實施方式相同之方法固定,以使半透膜22不因水的流動而移動。另,半透膜22亦較佳為設置在設於吸水口21內之多孔體上。作為這種多孔體,可使用上述之多孔體。 The
在供水裝置30中,多個單元20垂直堆疊於容器24上側。容器24容納供水至單元20之水。容器24垂直相交於垂直方向之方向上之截面之形狀並無特殊限制。例如,容器24可以是垂直相交於垂直方向之方向上之截面形狀為圓等圓筒狀者,或是垂直相交於垂直方向之方向之截面形狀為多角形等角柱狀者。作為容器24之材質,可列舉如不鏽鋼等金屬、玻璃、陶器等無機材料及各種樹脂等有機材料,並無特殊限制。 In the
單元20中,在容納之懸浮水之水面與單元20內壁之間形成空間27。於該空間27內中,在水面上方設有通氣孔23。透過如此設置通氣孔23,使單元20內,懸浮水之水面與單元20內壁之間形成之空間27之壓力為大氣壓。據此,即便堆疊多個單元20,亦可根據單元20之堆疊防止水位差增大,並使水位差保持為一段之單元20。透過如此在單元20中設置通氣孔23,可使水位差保持較小之狀態,因此與沒有設置通氣孔之情況相較,透過堆疊單元20可使揚程提高。 In the
在相鄰之單元20彼此連通之單元20下端設置的吸水口21,被浸泡在下側相鄰之單元20之懸浮水之澄清層26中。此外,與容器24上側相鄰之單元20之吸水口21,被浸泡在容器24內容納之水中。分別容納於單元20之懸浮水的量,被調整為使通氣孔23位於懸浮水之澄清層26之水面上方。此外,設置在單元20下方突出設置之吸水口21內的半透膜22,透過位於下側之單元20內之澄清層26之水與多孔體接觸。如此, 半透膜22將單元20內容納之懸浮水之澄清層26的水與堆積於該單元20上側相鄰之單元20之半透膜22上的堆積層25隔開。此外,容器24中容納之水量,調整為使該容器24上側相鄰之單元20之下方突出設置之吸水口21與容器24之水接觸。另,容器24透過外部儲水槽(無圖示)與軟管等連結管進行連結,當容器24內之水因供水而減少時,水從外部儲水槽抽出以補充減少之水量,使容器24內之水位維持恆定者亦佳。 The
如上述,藉由適當調整各單元20之懸浮水量,設置於吸水口21內之半透膜22,可將單元20內容納之懸浮水之堆積層25的水與單元20下側相鄰之單元20之懸浮水之澄清層26的水隔開。此外,藉由適當調整容器24內之水量,設置於吸水口21內之半透膜22,可將單元20內容納之懸浮水與單元20下側相鄰之容器24之水隔開。 As described above, by appropriately adjusting the amount of suspended water of each
在供水裝置30中,例如,預先在各單元20中,於下端吸水口21內之規定位置設置多孔體,並於其上設置半透膜22。之後,將懸浮水容納於單元20內時,由於容納之懸浮水向下側流動,使半透膜22與多孔體濕潤,水變得容易從下側吸入。單元內容納之懸浮水量,由以下情況決定:除了使該單元20上側相鄰之單元20之吸水口21內設置的半透膜22透過多孔體接觸滲透過的水之外,亦使通氣孔23位於懸浮水之水面上方。決定懸浮水量後,在位於最下側之單元20內填充規定量之懸浮水。之後,在容納懸浮水之單元20上方,堆疊新的單元20。將規定量之懸浮水填充至堆疊之單元20內。以下重複單元20之堆疊,及規定量之懸浮水之填充。另,在供水裝置30中,堆疊之單元20之數量可被稱為“段數”。例如,在容器24之上側,堆疊有2個單元20時,稱為“2段之供水裝置”,在堆疊有3個單元20時,稱為“3段之供水裝置”,以下,在堆疊有N(2個以上)個單元20時,稱為“N段之供水裝置”。 In the
在供水裝置30中,同樣地,單元20所容納之懸浮水中所含粒子沈降在半透膜22上形成粒子之堆積層25,並於其上形成上清液即澄清層26。 In the
本實施方式之供水裝置30中,在形成堆積層之各單元20中,根據圖2說明之機制產生水的上升流。在堆疊之單元20中位於最底部之單元20內,與下側相鄰之容器24內的水通過半透膜22上升至單元20內。上升至單元20內的水,進一步上升至與該單元20上側相鄰之單元20內。以下依序,水向更上側相鄰之單元20內上升。如此,容器24內的水就會上升至堆疊了多個單元20之供水裝置30之頂部,從流出口28流出。另,堆積層中粒子1之有效重力變得等於流體效力與斥力產生之互斥力之和,而形成平衡狀態(動態平衡),膨脹停止,而得以向上持續供水。 In the
(4)供水方法 (4) Water supply method
本發明之供水方法之一實施方式,具備以下步驟:於水中填充有粒子分散之懸浮水,將下端設有半透膜之單元沿垂直方向堆積;使位於最下部之單元之半透膜接觸該單元下端相鄰之水;以及,以沈降堆積於各單元內之半透膜上之粒子之電雙層重疊產生之滲透壓為驅動源,從各單元下端相鄰之水透過半透膜向上供水。本實施方式之供水方法,可藉由使用上述實施方式之供水裝置而達成。 An embodiment of the water supply method of the present invention includes the steps of: filling water with particle-dispersed suspension water, stacking a unit with a semi-permeable membrane at the lower end in a vertical direction; contacting the semi-permeable membrane of the unit at the bottom The water adjacent to the lower end of the unit; and, the osmotic pressure generated by the overlapping of the electric double layer of the particles deposited on the semi-permeable membrane in each unit as the driving source, and the upward supply of water from the adjacent water at the lower end of each unit through the semi-permeable membrane . The water supply method of this embodiment can be achieved by using the water supply device of the above embodiment.
[實施例] [Example]
以下依據實施例對本發明進行具體說明,唯本發明並不限於諸等實施例。 The present invention will be specifically described below based on embodiments, but the present invention is not limited to the embodiments.
首先,針對本發明之供水裝置之供水機制之確認實驗進行說明。 First, the confirmation experiment of the water supply mechanism of the water supply device of the present invention will be described.
[供水機制確認實驗] [Confirmation experiment of water supply mechanism]
圖7係示意性地表示用於供水機制之確認實驗之實驗裝置之截面圖。如圖7所示,在裝有蒸餾水之內徑20mm、長度200mm之丙烯酸樹脂製傳輸管71與內徑20mm、長度200mm之丙烯酸樹脂製沈降管72之間,配置膜濾網73(孔徑:0.2μm、材質:纖維素混合酯)。於傳輸管71底部安裝壓力感測器(無圖示)。壓力感測器量測了管底位置之水壓。此外,於儲水槽74填充蒸餾水79,並使用連結管75與傳輸管71連通。透過電子天秤(無圖示)秤量儲水槽74之重量,並計測被負壓吸入之水量。連結管75保持開放狀態。 FIG. 7 is a cross-sectional view schematically showing an experimental device used for the confirmation experiment of the water supply mechanism. As shown in FIG. 7, a membrane filter 73 (aperture diameter: 0.2) is arranged between the acrylic resin transfer tube 71 containing distilled water and having an inner diameter of 20 mm and a length of 200 mm and an acrylic
將易燒結氧化鋁(住友化學社製AES11E(商品名稱)、平均粒徑:0.48μm)分散於沈降管72內之膜濾網73上,調製成泥漿。泥漿係將所使用的氧化鋁粉體、蒸餾水、分散劑HCl依規定量混合,以球磨機混合1小時後,將泥漿進行真空脫泡供實驗使用。將泥漿之初期濃度調整為20vol%。此外,使泥漿之初期水位差△h0(沈降管72內泥漿液面與儲水槽74內蒸餾水水面之間之差)為90mm。泥漿分離為堆積層76、泥漿層77及澄清層78。氧化鋁粒子在泥漿中呈分散狀態。 Easily sintered alumina (AES11E (trade name) manufactured by Sumitomo Chemical Co., Ltd., average particle diameter: 0.48 μm) was dispersed on the
探討泥漿之pH值與壓力之關係。圖8係泥漿之pH值與靜水壓之關係圖。圖8係在圖7之實驗裝置中使用易燒結氧化鋁(平均粒徑:0.48μm),將初期濃度調整為20vol%,初期水位差△h0=90mm之泥漿pH值分別調整為6.8、6.4、5.7、4.2後,顯示量測靜水壓之結果。根據圖8之結果,顯示pH值愈低,靜水壓與大氣壓(0kPa)之間愈產生差距。 Explore the relationship between the pH of the mud and the pressure. Figure 8 is a graph of the relationship between the pH of the mud and the hydrostatic pressure. Fig. 8 is the use of easily sinterable alumina (average particle size: 0.48μm) in the experimental device of Fig. 7, the initial concentration is adjusted to 20 vol%, and the pH value of the mud with initial water level difference △h 0 =90mm is adjusted to 6.8 and 6.4 respectively After 5.7 and 4.2, the result of measuring the hydrostatic pressure is displayed. According to the results in FIG. 8, it is shown that the lower the pH value, the greater the difference between the hydrostatic pressure and the atmospheric pressure (0 kPa).
此外,還探討了泥漿之pH值與氧化鋁粒子之位能之關係。圖9係泥漿之pH值與氧化鋁粒子之位能之關係圖。圖9係在圖7之實驗裝置中使用易燒結氧化鋁(平均粒徑:0.48μm),將初期濃度調整為20vol%,初期水位差△h0=90mm之泥漿pH值分別調整為6.8、6.4、5.7、4.2後,運用DLVO 理論,顯示算出粒子表面間距離與位能之關係之結果。根據圖9之結果,顯示pH值愈低,位能曲線之峰值愈尖銳,表示粒子間斥力愈強。 In addition, the relationship between the pH of the mud and the potential energy of the alumina particles was also discussed. Fig. 9 is a graph showing the relationship between the pH value of mud and the potential energy of alumina particles. Fig. 9 is the use of easily sinterable alumina (average particle size: 0.48μm) in the experimental device of Fig. 7, the initial concentration is adjusted to 20 vol%, and the pH value of the initial water level difference Δh 0 = 90mm is adjusted to 6.8 and 6.4 respectively After 5.7 and 4.2, the DLVO theory is used to show the result of calculating the relationship between the distance between particle surfaces and potential energy. According to the results in Fig. 9, it is shown that the lower the pH value, the sharper the peak of the potential energy curve, indicating that the stronger the repulsion between particles.
使用圖7所示之實驗裝置,使連結管75呈開放狀態,探討水從儲水槽74通過傳輸管71供水至沈降管72為止之時間與靜水壓、時間與吸水速度之關係。使用之泥漿種類、泥漿濃度、初期泥漿之初期水位差△h0與該實驗條件相同。圖10係時間與靜水壓之關係及時間與吸水速度之關係圖。在圖10中,虛線表示時間與靜水壓之關係,實線表示時間與吸水速度之關係。如圖10所示,即便將傳輸管71與儲水槽74之間的連結管75保持開放,在實驗開始後,儘管水被排出一段時間,但從中途開始吸水。即顯示,即便剛開始連結管75關閉,在傳輸管71及沈降管72之系統中不確保負壓亦可進行吸水(供水)。據此,在供水之際,毋需負壓確保等操作,可簡便進行供水操作。 Using the experimental device shown in FIG. 7, the
在圖7之實驗裝置中使用易燒結氧化鋁(平均粒徑:0.48μm),調製初期濃度為45vol%之泥漿。初期水位差△h0=0mm及150mm時,使連結管75呈開放狀態,探討水從儲水槽74通過傳輸管71供水至沈降管72為止之時間與累積吸水量之關係、時間與平移能(位能)之關係。圖11係時間與平移能之關係及時間與累積吸水量之關係圖。在圖11中,虛線表示時間與平移能(位能)之關係,實線表示時間與累積吸水量之關係。如圖11所示,即便初期水位差△h0=0mm,亦有長時間持續供水。此外,初期水位差△h0=150mm時,顯示出長時間持續供水,及與初期水位差△h0=0mm時相較,其平移能更多。 In the experimental device of FIG. 7, easily sinterable alumina (average particle diameter: 0.48 μm) was used, and a slurry with an initial concentration of 45 vol% was prepared. When the initial water level difference △h 0 =0mm and 150mm, the connecting
供水實驗 Water supply experiment
(實施例1、2、比較例1) (Examples 1, 2 and Comparative Example 1)
接著,針對本實施方式之供水裝置之性能進行說明。圖12係用於性能 評價之供水裝置之照片。圖12所示之供水裝置,在圖3中被示意性地表示。如圖3所示,在裝有蒸餾水之內徑20mm、長度200mm之丙烯酸樹脂製傳輸管11上,下端設有膜濾網12(孔徑:0.2μm、材質:纖維素混合酯)之內徑20mm、長度30mm之丙烯酸樹脂製單元13堆疊成3段(實施例1)。於傳輸管11底部安裝壓力感測器(無圖示)。壓力感測器量測了管底位置之水壓。此外,於儲水槽C填充蒸餾水,並使用連結管D與傳輸管11連通。透過電子天秤秤量儲水槽C之重量,並計測被負壓吸入之水量。連結管D保持開放狀態。在單元13內容納泥漿。泥漿係將粒徑0.48μm之易燒結氧化鋁以HCl作為分散劑,以濃度45vol%、pH值4.3之條件混合,以球磨機混合1小時後再經真空脫泡調製而成。往單元13內之泥漿投入步驟,係先將泥漿投入後,於其上堆疊單元13並將單元13彼此接合,之後,將泥漿投入至單元13內。實施例1中之泥漿投入高度為90mm。將位於頂部之單元13之水面高度設定得較儲水槽C之水面高度更高,並將位於頂部之單元13內之泥漿水面高度與儲水槽C內之水面高度之間的差距作為”水位差“。使水位差為190mm。此外,在圖3中,將除了設置膜濾網12、膜濾網12等兩枚以外與實施例1之裝置相同之2段供水裝置(實施例2)、除了僅設置膜濾網12以外與實施例1之裝置相同之1段供水裝置(比較例1)用於實驗。 Next, the performance of the water supply device of this embodiment will be described. Figure 12 is a photograph of a water supply device used for performance evaluation. The water supply device shown in FIG. 12 is schematically shown in FIG. 3. As shown in FIG. 3, a membrane filter 12 (aperture diameter: 0.2 μm, material: cellulose mixed ester) has an inner diameter of 20 mm on an acrylic
測定結果如圖13及圖14所示。圖13係時間與靜水壓之關係圖。圖13顯示,相較於1段之供水裝置(比較例1),3段之供水裝置(實施例1)及2段之供水裝置(實施例2)即便不開放連結管D確保系統內的負壓,吸水還是從初期就進行,表示產生大的壓力差。因此,實施例1及實施例2之多段供水裝置與比較例1之1段供水裝置相較,其供水之驅動力更大,且即便是供水初期亦毋需確保負壓,故可透過簡便操作進行供水。圖14係水位差為19cm時,累積吸水量與時間之關係圖。實施例1之3段供水裝置,其 累積吸水量隨時間經過而增加,與此相對,比較例1之1段供水裝置,其累積吸水量在時間經過下還是維持0g,顯示沒有吸水。 The measurement results are shown in Fig. 13 and Fig. 14. Figure 13 is the relationship between time and hydrostatic pressure. Fig. 13 shows that, compared to the water supply device of the first stage (Comparative Example 1), the water supply device of the third stage (Example 1) and the water supply device of the second stage (Example 2) ensure that the negative pressure in the system is maintained even if the connection pipe D is not opened. Pressure, water absorption is still from the beginning, indicating that a large pressure difference occurs. Therefore, the multi-stage water supply device of Example 1 and Example 2 has a greater driving force for water supply than the one-stage water supply device of Comparative Example 1, and there is no need to ensure negative pressure even in the initial stage of water supply, so it can be easily operated through Provide water. Figure 14 shows the relationship between cumulative water absorption and time when the water level difference is 19cm. In the three-stage water supply device of Example 1, the cumulative water absorption increased with time. On the other hand, in the first-stage water supply device of Comparative Example 1, the cumulative water absorption remained at 0 g under time, indicating no water absorption.
粒子帶電符號之影響確認實驗 Confirmation experiment of the effect of charged symbols on particles
在供水機制確認實驗、實施例1、2之供水實驗所使用的易燒結氧化鋁為帶正電。為確認即便使用帶負電之粒子亦可進行供水操作,進行了以下實驗。 In the water supply mechanism confirmation experiment, the easily sintered alumina used in the water supply experiments of Examples 1 and 2 is positively charged. To confirm that the water supply operation can be performed even with negatively charged particles, the following experiment was conducted.
(實施例3) (Example 3)
圖15係示意性地表示用於粒子帶電符號之影響確認實驗之吸水裝置40之截面圖。如圖15所示,配置有容納離子交換水44之儲水槽45,以及投入泥漿42之單元41。在從儲水槽45底部沿垂直方向突出設置之凸部46,支撐投入泥漿42之單元41。在單元41內之底面設有開口部,於該開口部中,膜濾網43(孔徑:0.2μm、材質:纖維素混合酯)以成為單元41內之泥漿42與儲水槽45內之離子交換水44之間之邊界之方式設置。將從設置於單元41底面之膜濾網43到泥漿42液面為止之垂直方向距離h,作為泥漿投入高度。 FIG. 15 is a cross-sectional view schematically showing a water-absorbing
使用之泥漿,係使用離子交換水作為分散媒,將粒徑(d50)為0.52μm之氧化鈦(富士鈦工業社製TA-300、3.90g/cm3)分散,以濃度45vol%、pH值6(ζ=-55mV)之條件混合,使用球磨機混合1小時,再透過真空脫泡進行調製。泥漿之投入高度h分別為1.0cm、2.0cm、3.0cm。 The slurry used was ion-exchanged water as the dispersion medium, and titanium oxide (TA-300, 3.90 g/cm 3 manufactured by Fuji Titanium Industry Co., Ltd.) with a particle size (d 50 ) of 0.52 μm was dispersed at a concentration of 45 vol% and pH The value 6 (ζ=-55mV) was mixed under the condition of a ball mill for 1 hour, and then prepared by vacuum degassing. The input height h of the mud is 1.0 cm, 2.0 cm, and 3.0 cm, respectively.
測定結果如圖16所示。圖16係累積吸水量與時間之關係圖。由圖16可知,即便使用帶負電之氧化鈦粒子泥漿,亦顯示出累積吸水量增加且進行吸水之結果。此外,顯示隨著泥漿投入高度增加,累積吸水量亦增加。另,泥漿投入高度為3.0cm時,累積吸水量減少,推測為水位差之影響。 The measurement results are shown in Figure 16. Figure 16 shows the relationship between cumulative water absorption and time. As can be seen from FIG. 16, even if the negatively charged titanium oxide particle slurry is used, the cumulative water absorption amount increases and water absorption results. In addition, it shows that as the mud input height increases, the cumulative water absorption also increases. In addition, when the slurry input height is 3.0 cm, the cumulative water absorption decreases, presumably due to the effect of the water level difference.
高分子電解質吸附粒子之供水確認實驗 Water supply confirmation experiment of polymer electrolyte adsorbed particles
使用圖15所示之吸水裝置,確認透過吸附高分子電解質之粒子進行供水。使用之泥漿,係將粒徑(d50)為0.48μm之易燒結氧化鋁(AES-11E、3.96g/cm3)與作為高分子電解質之多羧酸銨(PCA、Serna D-305),以離子交換水作為分散媒,混合至多羧酸銨之有效成分濃度為40wt%、氧化鋁之粒子濃度為45vol%為止,使用球磨機混合1小時,再透過真空脫泡進行調製。相對於1g氧化鋁,以3.6mg之比例添加多羧酸銨。另,在圖15之吸水裝置中,使泥漿之投入高度為2.0cm。 Using the water absorption device shown in FIG. 15, it was confirmed that water was supplied through the particles adsorbing the polymer electrolyte. The mud used is made of easily sintered alumina (AES-11E, 3.96g/cm 3 ) with a particle size (d 50 ) of 0.48 μm and ammonium polycarboxylate (PCA, Serna D-305) as a polymer electrolyte. Using ion-exchanged water as the dispersion medium, mix until the effective component concentration of the ammonium polycarboxylate is 40 wt% and the particle concentration of alumina is 45 vol%, mix for 1 hour using a ball mill, and then prepare by vacuum defoaming. Ammonium polycarboxylate was added in a ratio of 3.6 mg to 1 g of alumina. In addition, in the water absorption device of FIG. 15, the input height of the slurry is 2.0 cm.
測定結果如圖17所示。圖17係累積吸水量與時間之關係圖。由圖17可知,通常透過粒子表面帶正電之易燒結氧化鋁粒子上吸附作為高分子電解質之多羧酸銨,使氧化鋁粒子表面帶負電,即便如此仍顯示累積吸水量增加,且有進行吸水。 The measurement results are shown in Fig. 17. Figure 17 is the relationship between cumulative water absorption and time. As can be seen from FIG. 17, the ammonium polycarboxylate as a polymer electrolyte is usually adsorbed on the easily sinterable alumina particles that are positively charged on the surface of the particles, and the surface of the alumina particles is negatively charged. Even so, the cumulative water absorption is increased and there is progress. Absorb water.
粒子濃度之影響確認實驗 Confirmation experiment of the effect of particle concentration
使用圖15所示之吸水裝置,確認使泥漿中之粒子濃度發生變化時對吸水性能之影響。使用之泥漿,係將粒徑(d50)為0.52μm之易燒結氧化鋁(AES-11E、3.96g/cm3),以離子交換水作為分散媒進行分散,使濃度為20vol%、45vol%,並使用HCl作為pH值調整劑,調整至pH值3(ζ=60mV)之條件進行混合,使用球磨機混合1小時,再透過真空脫泡進行調製。 Using the water absorption device shown in Fig. 15, the influence on the water absorption performance when the particle concentration in the mud is changed is confirmed. The mud used is to disperse easily sintered alumina (AES-11E, 3.96g/cm 3 ) with a particle size (d 50 ) of 0.52 μm, using ion-exchanged water as the dispersion medium, so that the concentration is 20vol%, 45vol% , And using HCl as a pH adjusting agent, adjusted to pH 3 (ζ=60mV) and mixed, mixed using a ball mill for 1 hour, and then prepared by vacuum defoaming.
測定結果如圖18所示。圖18係累積吸水量與時間之關係圖。圖18顯示,粒子濃度愈大,累積吸水量愈增加。 The measurement results are shown in Figure 18. Figure 18 is the relationship between cumulative water absorption and time. Figure 18 shows that the larger the particle concentration, the greater the cumulative water absorption.
泥漿投入高度之影響確認實驗 Confirmation experiment of the influence of mud input height
使用圖15所示之吸水裝置,確認泥漿投入高度發生變化時對吸水性能之影響。使用之泥漿,係將粒徑(d50)為0.48μm之易燒結氧化鋁(AES-11E、3.96g/cm3),以離子交換水作為分散媒進行分散,使濃度為45vol%, 並使用HCl作為pH值調整劑,調整至pH值3(ζ=60mV)之條件進行混合,使用球磨機混合1小時,再透過真空脫泡進行調製。在圖15中,將泥漿投入高度h變化為0.25cm、0.50cm、1.0cm、2.0cm、3.0cm。 Use the water absorption device shown in Figure 15 to confirm the effect of the slurry input height on the water absorption performance. The mud used is to disperse easily sintered alumina (AES-11E, 3.96g/cm 3 ) with a particle size (d 50 ) of 0.48 μm using ion-exchanged water as the dispersion medium, so that the concentration is 45 vol%, and use HCl is used as a pH adjusting agent, adjusted to pH 3 (ζ=60mV) and mixed, mixed using a ball mill for 1 hour, and then prepared by vacuum defoaming. In FIG. 15, the slurry input height h is changed to 0.25 cm, 0.50 cm, 1.0 cm, 2.0 cm, and 3.0 cm.
測定結果如圖19所示。圖19係累積吸水量與時間之關係圖。圖19顯示,泥漿投入高度愈高,其累積吸水量亦隨之增加。另,泥漿高度為3.0cm時,累積吸水量減少,推論其原因為水位差。 The measurement results are shown in Fig. 19. Figure 19 is the relationship between cumulative water absorption and time. Figure 19 shows that the higher the mud input, the higher the cumulative water absorption. In addition, when the mud height is 3.0 cm, the cumulative water absorption decreases, which is inferred to be due to the water level difference.
[產業上之可用性] [Industry availability]
本發明之供水裝置及供水方法,可作為供水之供水裝置及供水方法使用。 The water supply device and water supply method of the present invention can be used as a water supply device and water supply method for water supply.
20‧‧‧單元 20‧‧‧ unit
21‧‧‧吸水口 21‧‧‧Suction port
22‧‧‧半透膜 22‧‧‧ Semi-permeable membrane
23‧‧‧通氣孔 23‧‧‧ vent
24‧‧‧容器 24‧‧‧Container
25‧‧‧堆積層 25‧‧‧Stacked layer
26‧‧‧澄清層 26‧‧‧Clarification layer
27‧‧‧空間 27‧‧‧Space
28‧‧‧流出口 28‧‧‧ Outflow
30‧‧‧供水裝置 30‧‧‧Water supply device
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