Although wastewater is commonly viewed as a problematic “waste” stream, it often contains large amounts of compounds that could be put to beneficial use. For example, residential wastewater is an abundant source of nutrients, such as nitrogen, phosphorous, and potassium. These nutrients are major components of synthetic fertilizers typically used in agricultural and horticultural applications. If such nutrients could be economically harvested from wastewater and made available to end users at low cost, they could be of great benefit to those end users, particularly in arid regions where poor soil conditions exist.
Wastewater is typically treated before being released to the environment as untreated wastewater can cause environmental degradation. For example, wastewater is often treated in wastewater treatment (WWT) plants to remove its organic compounds and nutrients. The organic compounds are typically removed using biological processes, while the nutrients are removed through additional process operations. Nutrient removal processes impose additional costs. Additionally, nutrients that are removed through these operations become unavailable for use in agricultural or horticultural processes.
Existing methods for the recovery and reuse of nutrients from wastewater have inherent drawbacks. Precipitation-based approaches, such as the formation of magnesium ammonium phosphate (struvite) and calcium phosphate, often require elevated pH, high nutrient concentrations, addition of additional chemicals (e.g., magnesium oxide), subsequent dewatering and drying, and handling/packaging, which adds to the costs. Another approach is the direct use of partially-treated and disinfected wastewater for plant irrigation without prior removal of nutrients (direct fertigation). Such methods are appealing since the nutrients are preserved in the irrigation water and utilized efficiently. However, direct fertigation requires that the demand (i.e., end user) be physically located near the supply (wastewater source). This is something that is often not possible or practical.
In view of the above discussion, it can be appreciated that it would be desirable to have a low-cost system and method for recovering nutrients from nutrient sources, such as a wastewater, and making such nutrients available to end users in agricultural or horticultural processes.
The present disclosure may be better understood with reference to the following figures. Matching reference numerals designate corresponding parts throughout the figures, which are not necessarily drawn to scale.
As described above, it would be desirable to have a low-cost system and method for recovering nutrients from nutrient sources, such as a wastewater, and making such nutrients available to end users in agricultural or horticultural processes. Disclosed herein are examples of such systems and methods. In one embodiment, a system comprises reusable nutrient cartridges that are configured to adsorb nutrients from a nutrient stream and then used at an agricultural or horticultural site as a fertilizer source. In some embodiments, the cartridges can be “charged” with nutrients at a nutrient source site by flowing a nutrient stream through the cartridge, delivered to an end use site, used to fertilize crops or other plants at the end use site by flowing water through the charged cartridge (thereby “discharging” the cartridge), and then returned to the nutrient source site for recharging. The cartridge can then be reused in this manner again and again until the end of its useful life. Although the system is scalable, in some embodiments, the cartridges are relatively small in size so as to facilitate easy delivery to the end use site, which may be remote from the nutrient source site.
In the following disclosure, various specific embodiments are described. It is to be understood that those embodiments are example implementations of the disclosed inventions and that alternative embodiments are possible. All such embodiments are intended to fall within the scope of this disclosure.
Disclosed herein are nutrient recovery systems employing compact, reusable nutrient cartridges capable of capturing nutrients from nutrient streams and subsequently releasing them in desired, targeted streams. The cartridges utilize ion exchange and adsorptive materials to selectively capture pertinent nutrient material from the nutrient streams, thereby providing a method for low-cost nutrient removal. The cartridges, once charged with nutrient material, subsequently release nutrients where desired serving as a passive, low-cost technology for nutrient removal and fertigation. The cartridges house ion exchange and adsorptive media in combination with filter material to achieve a flow-through design. In some embodiments, an indicator is used to indicate the level of nutrient charge (i.e., nutrient concentration) within the cartridge. Consequently, the disclosed systems enable passive nutrient recovery, effectively alleviating problems associated with the lack of access to pertinent nutrient resources necessary for remote agricultural operations in non-ideal locations.
With further reference to
At that point, the reusable nutrient cartridge 14 can be delivered to an end use site 18 at which it will be “discharged.” Such discharging comprises flowing water through the cartridge 14 to release the nutrients contained in the cartridge and produce a dilute nutrient solution that can be used to simultaneously irrigate and fertilize, or fertigate, crops or other plants. This process is illustrated in
Completing the discharge phase readies the reusable nutrient cartridge 16 for a new charging phase. Accordingly, once the cartridge 16 has been fully discharged at the end use site 18, it is ready for another charge cycle and can be returned to the nutrient source 12 for this purpose. The above-described cycle can be repeatedly performed throughout the useful life of the cartridge 14, 16.
The nutrient source 12 and the end use site 18 may be remote of each other. For this reason, the reusable nutrient cartridges 14, 16 can be relatively small to enable them to be easily delivered between the nutrient source 12 and the end use site 18. By way of example, the cartridges 14, 16 can have a volumetric capacity of approximately 1 to 5 L. In such cases, a variety of distribution methods are possible, including delivery by land vehicle as well as by unmanned aerial vehicles (UAVs). It is noted, however, that the nutrient source 12 and the end use site 18 may be located close to each other, and even at the same site. For example, the nutrient source 12 could be located at one's home and the end use site could be a yard or greenhouse of the home. In such cases, the cartridge 14, 16 can be a fixed installation, in which case delivery is unnecessary. In that scenario, the cartridge 14, 16 could be submerged in a reservoir where the nutrients accumulate (e.g., septic tank, fish pond, aquaculture tank, or storm water retention pond), thus providing a nutrient sink.
As shown in
With reference to
In some embodiments, the reusable nutrient cartridge can include a charge indicator that provides an indication of the level of nutrient concentration within the cartridge.
This application is the 35 U.S.C. § 371 national stage application of PCT Application No. PCT/US2017/43327, filed Jul. 21, 2017, where the PCT claims priority to U.S. Provisional Application Ser. No. 62/365,729, filed Jul. 22, 2016, both of which are herein incorporated by reference in their entireties.
This invention was made with Government support under grant contract number RD835569 awarded by the National Science Foundation and 1243510 awarded by the National Science Foundation. The Government has certain rights in the invention.
Filing Document | Filing Date | Country | Kind |
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PCT/US2017/043327 | 7/21/2017 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
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WO2018/017975 | 1/25/2018 | WO | A |
Number | Name | Date | Kind |
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4750512 | Craig | Jun 1988 | A |
4957134 | Craig | Sep 1990 | A |
5178181 | Craig | Jan 1993 | A |
5656159 | Spencer | Aug 1997 | A |
5660802 | Archer | Aug 1997 | A |
5820762 | Bamer | Oct 1998 | A |
6524540 | Heinig, Jr. | Feb 2003 | B1 |
7186333 | Kluge | Mar 2007 | B2 |
7588744 | Sylvester | Sep 2009 | B1 |
8759251 | Long | Jun 2014 | B2 |
9051192 | Kent | Jun 2015 | B2 |
9462745 | Jivanjee, Jr. | Oct 2016 | B1 |
10322956 | Whiteman | Jun 2019 | B2 |
10549245 | Freudenberg | Feb 2020 | B2 |
20080073277 | Paoluccio | Mar 2008 | A1 |
20100193416 | Barbaro | Aug 2010 | A1 |
20110309024 | Athanasiadis | Dec 2011 | A1 |
20120091070 | Sjauta | Apr 2012 | A1 |
20130233802 | Viswanathan | Sep 2013 | A1 |
20130299429 | Connaughton | Nov 2013 | A1 |
20140027362 | Kent | Jan 2014 | A1 |
20160016127 | Mentzel | Jan 2016 | A1 |
20180105437 | Beierwaltes | Apr 2018 | A1 |
Number | Date | Country |
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W2016025109 | Feb 2016 | WO |
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Number | Date | Country | |
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20190276334 A1 | Sep 2019 | US |
Number | Date | Country | |
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62365729 | Jul 2016 | US |