The present invention relates to methods and apparatus for producing minerals or other precipitable substances including salt by precipitation from a water source by the application of solar radiation. The water source might be sea water when the intention is to product salt.
It is known to introduce sea or saline water into a shallow bed subject to solar radiation over a period of time during which the water is evaporated off leaving crystalline salt (NaCl) that can be collected and used as required. Such arrangements are well known but are subject to introduction of impurities from the environment and from the production techniques. The objective of the present invention is to provide an improved method of producing conventional salt (NaCl), and other salts or precipitable substances from a liquid source including sea water, ground water and industrial or other commercial water sources including waste water that might otherwise be discharged into the environment. A particularly preferred objective of this invention is to provide a method as aforesaid with substantially no waste water or liquid discharge. A further objective is to provide improved apparatus for use in the aforesaid methods.
According to a first aspect of this invention there is provided a method of producing a precipitable substance from a feed liquid source, the method including the steps of:
Other features of the above method may be as defined in claims 2, 3, 4 and 5 as annexed hereto, the subject matter of these claims being included in the disclosure of this specification by this reference thereto.
In accordance with a further aspect of the present invention there is provided a method of producing one or more precipitable substances from a feed liquid source in precipitation apparatus, the method including the steps of:
Conveniently, solar radiation levels directed to the first solar energy treatment arrangement are sensed and at least the volume of the liquid from the feed liquid source is adjusted in response to sensed radiation levels. Flow volumes of the treatment liquid may also be adjusted in response to any one or more of sensed atmospheric conditions including temperature, humidity or wind levels.
Preferably a flow volume rate of the liquid delivered to the or each first treatment arrangement is measured, the or each first treatment arrangement also producing a clean water condensate flow with the flow volume rate of the clean water condensate from the or each first treatment arrangement also being measured, the density of the liquid discharged from the or each treatment panel being determined from the measure of flow volume rates.
In an embodiment, the above described method may include at least two solar energy treatment arrangements in the first solar energy treatment stage, the or each first solar energy treatment arrangement being arranged to receive the liquid discharged from either feed liquid source or a preceding first solar energy treatment arrangement in the first solar energy treatment stage, the solar radiation passing through the upper solar energy transmission wall of the or each treatment panel construction of the or each first solar energy treatment arrangement further concentrating the precipitable substance or substances in the liquid within the or each treatment panel construction.
Conveniently, the density level of the liquid discharged from the or each first solar energy treatment arrangement is sensed, and if the sensed density level is less than a desired predetermined level, the discharged liquid is returned to an inlet region of the or a preceding first solar energy treatment arrangement.
In an arrangement, at least a proportion of the liquid discharged from a first solar energy treatment arrangement is collected to separately precipitate a precipitable substance therefrom, any liquid remaining from the separate precipitation being returned to the first solar energy treatment stage or to the final solar energy treatment arrangement. Conveniently, any liquid remaining from separate precipitation of the precipitable substance is returned to the precipitation apparatus utilized in the aforesaid method, for further processing.
In an arrangement, in one or more of the first or further solar energy treatment arrangements includes structure to condense water evaporated from the liquid and to collect the condensed water as a clean water discharge.
The feed liquid source may be any source containing dissolved substances capable of being precipitated therefrom including but not limited to sea or other saline water, ground water, and contaminated water from industrial or other commercial processes. The precipitable substances include, but are not limited to salt (NaCl), MgCl2, sodium bicarbonate, gypsum, minerals, and metals.
Preferably, the method provides zero waste liquid discharge, i.e. the liquid is consumed in the final solar energy treatment arrangement. If any liquid remains, it is collected and either returned or further separately processed to recover useful substances therefrom.
In accordance with a further aspect, the present invention also provides a panel construction for the production of a precipitable substance or substances from a feed liquid source, the panel construction including:
Conveniently, the panel construction includes flow control apparatus to control the flow of the treatment liquid to the surface region. Conveniently, the treatment liquid flow rate is arranged to flow at an average flow rate of about 3 litres/square meter/hour. Preferably the control means is adjusted in response to solar sensed solar radiation levels impinging on the upper solar energy transmission wall, that is the flow rate of the treatment liquid is increased if the sensed solar radiation levels is relatively higher. In an embodiment the density of any treatment liquid discharged from the panel construction is tested and if below a predetermined level, the discharged treatment liquid is returned to an inlet flow to the panel construction.
In an embodiment, the upper solar energy transmission wall is removable from the treatment member. The upper solar energy transmission wall might include fixing means to enable the wall to be operationally fixed to the treatment member, but removed when desired. Conveniently, air flow means is provided to allow air flow through the panel construction. Preferably air flow is arranged to flow in the direction of flow of the treatment liquid over the treatment member. Conveniently, any air flow openings associated with the air flow means include coverings providing no or only limited restrictions to air flow but preventing ingress of other unwanted contaminants.
Conveniently, the treatment member is a tray, the surface region is an upwardly facing surface of a base wall of the tray, and the treatment liquid is retained on the surface region by upstanding perimeter walls along at least side edge regions of the base wall of the tray. Preferably the tray is formed from a metal foil or plastics material. Conveniently, a porous layer may be positioned on the base wall of the tray. The tray may include transversely extending corrugations located between side edge regions of the base wall.
Several embodiments of the present invention may be as disclosed in the annexed drawings and further described with reference thereto hereinafter.
Referring to
Conveniently, a solar energy sensor 46 might be provided to sense the level of solar energy radiation impinging on the panel constructions 42, the sensed level being used to control the flow control device 44. The treatment liquid discharged from the panel constructions 42 are collected and tested for density levels via a sensor 51 to ensure that the density level has reached a first predetermined level. If it is below the first predetermined level, it is recycled by being returned via a valve means 47 to a position upstream of the flow control device 44. If desired a proportion of the treatment liquid discharged that is at or above the first predetermined level might be diverted via the valve means 47 to a separate process unit 48 to recover solids content in the concentrated liquid.
The treatment liquid discharged from the first solar energy treatment arrangement 41 may be delivered via line 48 and a flow control device 49 to a further solar energy treatment arrangement 50. Again the arrangement 50 may be comprised of at least one but possibly multiple further treatment panel constructions 52 which again can be manufactured as described in International Patent Application Nos. PCT/AU2009/000503 and PCT/AU2010/001533. Again a sensor 51 senses density levels of the liquid discharged from the panel construction or constructions 52 and the sensor 51 controls the valve means 47 to either return treatment liquid to an inlet zone of the further first solar energy treatment arrangement 50 or to pass the treatment liquid on to a further alternative treatment stage 48 via line 55 if the density level is at or above a predetermined level. Further treatment stages 60, 70, 80 may be provided where like features in the further first solar energy treatment arrangement 50 have been given the same reference numerals. At each stage 50, 60, 70 or 80, it is possible, but not essential, that the treatment liquid might be diverted to a separate treatment process 56, 66, 76 or 86 to recover any desirable substances in the concentrated treatment liquid. Instead of sensors 51, the volume flow rate of treatment liquid delivered and the volume flow rate of clean water condensate exiting via lines 45 might be used to determine liquid density at each of the valve means 47.
While
Treatment liquid leaving the final further stage 80 via line 81 passes, preferably via a flow control device 49 to a treatment panel construction 10 (as described hereafter) or a pair of such panel constructions 10, 10′. While two such panel constructions 10, 10′ are illustrated further such panel constructions 10 (or 10′) could be employed. If the apparatus 40 is intended to process sea water as the feed liquid source 43, the first panel 10 is adapted to precipitate salt (NaCl) when the treatment liquid has a concentration level of 1.18 to 1.25 with any remaining treatment liquid being transferred to a subsequent panel construction 10 or ultimately to a panel construction 10′ for MgCl2 to be recovered from liquid at a concentration level of about 1.35. If desired and if there is any remaining treatment liquid it might simply be collected and processed separately. Conveniently again the discharged liquid density level may be tested at 51 and returned for reprocessing if the concentration is below the level required to precipitate NaCl, in the potential example given. Again solar energy radiation sensors 46 might also be employed to control entry flow rates via control devices 49 to maintain the density of the liquid passing into the panel construction 10, 10′ at the required level to precipitate the required substance (typically NaCl with sea water as the feed liquid). Liquid density levels at 51 might alternatively be measured by measuring liquid volume flow rates in (for example) at 49, and out (for example) at 51. Treatment liquid may be pumped, if required around the apparatus 40 but preferably gravitational flows are desirable to minimize power consumption. Conveniently, at each stage 50, 60, 70 or 80 discharged treatment liquid might be diverted for separate treatment in suitable devices 56, 66, 76 or 86 to recover desirable substances in the liquid.
Referring to
In use, the panel construction 10 is suitably supported in the open with the upper wall 15 facing upwardly and subject to available solar energy radiation. The panel construction may be supported with a low angle of inclination, i.e. 0° to 5°. Sea or saline water or concentrated such water via apparatus shown in
The upper surface of the tray base wall 19 may have a hydrophilic surface (to the treatment liquid) to promote an even distributed film flow over the surface. Further, the construction may include a removable porous layer 26 covering substantially all of the surface. The salt formed on the production method of this invention may build up on the layer 26 and when sufficient salt has been formed, the layer 26 and the salt carried thereby can be removed by removing the upper wall 15. Thereafter the salt can be stripped from the layer 26 and the layer 26 can either be reused if it remains suitable for the task or it can be replaced with a new such layer. In a possible alternative the base wall 19 of the tray may include low profile ripple or corrugations 27 extending transversely across the tray 18. In this case, the salt builds directly on the base wall 19 and the tray 18 itself needs to be removed from the chamber 17 when the salt is to be stripped therefrom.
In a preferred arrangement (FIGS. 6/7), the lower end 30 of the tray base wall 19 may have no upright end wall permitting any excess treatment water to flow into a cavity 31 through an opening 34 in the end wall 14 to be discharged via line 24 and recycled as discussed earlier. It is preferred that air flow 32 be allowed to flow over the tray 18 between the two ends 13, 14 through suitable openings 33 formed therein. Conveniently, the depth of the tray 18 is reasonably high, about 200 to 600 mm, so that a reasonable quantity of salt can be formed before it is required to remove same from the panel construction 10. The panel construction might have a length of about two meters and a width of about one meter.
Number | Date | Country | Kind |
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2010901455 | Apr 2010 | AU | national |
The present application is a National Phase entry of PCT Application No. PCT/AU2011/000394, filed Apr. 7, 2011, which claims priority from Australian Patent Application No. 2010901455, filed Apr. 7, 2010, the disclosures of which are hereby incorporated by reference herein in their entirety.
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/AU2011/000394 | 4/7/2011 | WO | 00 | 1/15/2013 |