Abstract:Nanobubble technology, as an emerging and sustainable approach, has been used for remediation of eutrophication. However, the influence of nanobubbles on the restoration of aquatic vegetation and the mechanisms are unclear. In this study, the effect of nanobubbles at different concentrations on the growth of Iris pseudacorus (Iris) and Echinodorus amazonicus (Echinodorus) was investigated. The results demonstrated that nanobubbles can enhance the delivery of oxygen to plants, while appropriate nanobubble level… Show more
“…NBW may serve to enhance photosynthesis, stimulate GA hormone secretion, as well as affecting the distribution of microbial communities by increasing soil oxygen content which effectively promotes the absorption and transformation of nutrients by crops. (Wang et al, 2020;Zhou et al, 2020;Motoka et al, 2013;Wu et al, 2019). All of these factors further promoted yield increases.…”
A b s t r a c t. Improving crop yield and quality, as well as water and fertilizer use efficiency in a synergetic manner is a substantial challenge. It involves limits to the sustainable development of protected agriculture. Here, we propose a new irrigation method using nanobubble water through subsurface drip irrigation to improve the agricultural performance of crops. Experiments were conducted to evaluate the effects of nanobubble water on growth, yield, quality, irrigation water use efficiency, and the nitrogen partial productivity of greenhouse watermelon and muskmelon. The results showed that in nanobubble water conditions, reducing the amount of irrigation or fertilization by 20% had no negative impacts on the tested crops, instead there were increases in the yield, quality, irrigation water use efficiency and nitrogen partial productivity of the two crops. When irrigation and fertilization were both decreased by 20%, the irrigation water use efficiency was improved by 82.6 and 70.2%, the nitrogen partial productivity increased by 68.9 and 30.4%, vitamin C increased by 50.1 and 66.7% which was significant. This may be because nanobubble water reduced the redundant growth of crops, and promoted the balance between individual development and production. Moreover, nanobubble water finally achieved increased economic benefits by reducing the input of irrigation and fertilization. Therefore, we suggest that 80% irrigation and 80% fertilization with nanobubble water could be adopted for Cucurbitaceae in greenhouse conditions. This method also has reference significance for reducing agricultural water input.
“…NBW may serve to enhance photosynthesis, stimulate GA hormone secretion, as well as affecting the distribution of microbial communities by increasing soil oxygen content which effectively promotes the absorption and transformation of nutrients by crops. (Wang et al, 2020;Zhou et al, 2020;Motoka et al, 2013;Wu et al, 2019). All of these factors further promoted yield increases.…”
A b s t r a c t. Improving crop yield and quality, as well as water and fertilizer use efficiency in a synergetic manner is a substantial challenge. It involves limits to the sustainable development of protected agriculture. Here, we propose a new irrigation method using nanobubble water through subsurface drip irrigation to improve the agricultural performance of crops. Experiments were conducted to evaluate the effects of nanobubble water on growth, yield, quality, irrigation water use efficiency, and the nitrogen partial productivity of greenhouse watermelon and muskmelon. The results showed that in nanobubble water conditions, reducing the amount of irrigation or fertilization by 20% had no negative impacts on the tested crops, instead there were increases in the yield, quality, irrigation water use efficiency and nitrogen partial productivity of the two crops. When irrigation and fertilization were both decreased by 20%, the irrigation water use efficiency was improved by 82.6 and 70.2%, the nitrogen partial productivity increased by 68.9 and 30.4%, vitamin C increased by 50.1 and 66.7% which was significant. This may be because nanobubble water reduced the redundant growth of crops, and promoted the balance between individual development and production. Moreover, nanobubble water finally achieved increased economic benefits by reducing the input of irrigation and fertilization. Therefore, we suggest that 80% irrigation and 80% fertilization with nanobubble water could be adopted for Cucurbitaceae in greenhouse conditions. This method also has reference significance for reducing agricultural water input.
“…However, O 2 NBs could improve the organic fertilizer utilization by soil microbes that could indirectly support the plant growth by increasing the plant-available N and P . Moreover, O 2 NBs could enhance O 2 delivery to soil and promote the aerobic respiration of plants and the ROS generations, which could activate plant proliferative pathways . N 2 NBs seem to increase the soil nitrogen, which is the most limiting factor in the production of crop .…”
Irrigation
with gaseous nanobubble (NB)-containing water has been
demonstrated to promote seed germination and plant growth. To further
reveal the impacts of NBs on plant growth, this study compared soil
chemical properties and the release of soil elements (e.g., NH4
+, K+, and Mg2+) before and
after immersion with different gaseous NBs such as oxygen (O2), nitrogen (N2), hydrogen (H2), carbon dioxide
(CO2), and air. Exposure to NBs resulted in different influences
on the soil pH, dissolved oxygen (DO), redox potential, and nutrient
release. For instance, O2 NBs significantly increased both
DO and redox potentials of the treated soil. CO2 NBs increased
the release of Ca2+, Mg2+, and PO4
3– from the treated soil, whereas N2 NBs only improved the NH4
+ release from the
soil. Finally, multiple-factor correlation analysis and principal
component analysis revealed intercorrelations between the different
soil properties and confirmed that the nutrient ion release was highly
dependent on the type or composition of NBs.
“…The ecological effects of the NB treatments will also require further research. A study into the effects of NB treatments on aquatic macrophyte growth demonstrated beneficial effects up to a threshold above which plant growth was inhibited [52]. Yang et al [29] reported the non-toxicity of chitosan, the flocculant used in many recent MLS products, while an ecotoxicological study by Wang et al [34], on the effects of various flocculants with potential for use in MLS systems, determined chitosan and cationic starch dose rates that can be used with minimal adverse effects.…”
Section: Research Gaps and Recommendations For Future Researchmentioning
Nutrient enrichment of lakes from anthropogenic activities is a significant and increasing issue globally, impairing the health, biodiversity and service provisioning from lakes, with impacts on cultural, recreational, economic and aesthetic values. Internal nutrient loads from lakebed sediment releases are a primary cause of lake eutrophication and have necessitated geoengineering methods to mitigate releases and speed up recovery from eutrophication. Our objective in this review was to evaluate the use of oxygen nanobubbles as a geoengineering technology to remediate low oxygen conditions at the lake sediment/water interface, as a precursor to alleviating eutrophication linked to high internal nutrient loads. Oxygen nanobubbles (NBs) are bubbles < 1000 nm formed at the interface of solid surfaces and aqueous solutions. These bubbles have higher density than water, persist for longer and facilitate greater oxygen solubility than larger bubbles. Methods have been developed to enable NB formation at the surface of carrier materials, which are then used in conjunction with modified local soils (MLSs), to ‘floc, lock and oxygenate’ to strip nutrients from the water column, locking them in lakebed sediments and oxygenating the sediments to prevent re-release of nutrients. Most studies of NBs for lake restoration have thus far only demonstrated their potential for this purpose, using short-term, small-scale core incubations conducted mainly in laboratory settings. Work is required to (1) address scalability, including procurement and cost, (2) extend laboratory incubation studies to large outdoor enclosures and pond/lake trials, (3) examine longevity of the effects in the natural environment, including potential for MLSs to smother benthos and/or have toxic effects, and (4) extend to a range of lake environments and MLS types. Legal, cultural and social acceptance of the technology is another prerequisite of applications in the natural environment and requires individualised analysis. Until these issues are addressed in a systematic way that addresses scalability and recommends suitable carrier materials and MLSs, NBs may continue to remain largely untried as a geoengineering method to address lake eutrophication.
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