Progress 09/01/23 to 08/31/24
Outputs Target Audience:The target audience for the proposed research is vegetable growers, stakeholders, crop advisors, students, and the scientific community. The presentations/demonstrations were given at the Clemson graduate student research forum, Clemson graduate student research symposium, and will be presented at the upcoming ASA-CSSA-SSSA annual meeting in San Antonio, Texas (Nov. 2024). Further, initial results from the ongoing experiments were shared with specialty crop growers in South Carolina at the Edisto Research and Education Center's Watermelon field day. Project initiation was shared with growers, and stakeholders through social media and through a Clemson article. Further a manuscript was submitted to a scientific journal for publication. Changes/Problems:
Nothing Reported
What opportunities for training and professional development has the project provided?Project provided/providing interdisciplinary training to two PhD students. One student is getting trainedon the nutrient management, soil health and weed management aspect of the project involving fertilizer formulation, conducting lab incubation studies and measurement of nitrogen and phosphorus flux changes in soil. A second student is getting trained on soil borne disease management in specialty crops in the project. How have the results been disseminated to communities of interest?The project is utilizing the DAF solids produced by growers, Sedron solids produced by Sedron technologies (Sedro-Woolley, Washington) and rendering materials produced by Darling Ingredients Inc. (Irving, Texas). Further, project is utilizing the neem and karanja oil produced by Ahimsa Organics. The objective and the potential outcome of the project were communicated with the industry stakeholders through informal/formal talks. The results of the ongoing studies were presented to students and scientific audience at the Clemson graduate student research forum, Clemson graduate student research symposium, and will be presented at the upcoming ASA-CSSA-SSSA annual meeting in San Antonio, Texas (Nov. 2024). Further, initial results from ongoing experiments were communicated to the vegetable growers in South Carolina at the Edisto Research and Education Center's Watermelon field day. What do you plan to do during the next reporting period to accomplish the goals?From the initial laboratory experiments four best performing manure product-based (two) and rendered animal product-based (two) fertilizer formulations were selected for further studies. During the next reporting year, we will evaluate the selected best performing fertilizer formulations along with different plastic mulch types for anaerobic soil disinfestation (ASD) in greenhouse studies. Four different organic fertilizer formulations that are selected includes MBM, DAF, MBM with sulfur (25% of N) and DAF with neem oil (10% of N). We are evaluating three different plastic mulches including Via flex barrier (designed for bio-fumigation), black solar shrink (UV reactive), and conventional black mulch. The effect of treatments on soil fertility, soil health, plant growth and weed management will be evaluated. Further, first year field trails will be implemented in Spring 2025 using the selected fertilizer formulations and plastic mulch types at two locations in South Carolina.
Impacts What was accomplished under these goals?
Organic materials such as meat and bone meal (MBM; rendering product) and treated manure products [dissolved air flotation (DAF) solids] can be an excellent fertilizer due to balanced availability of nutrients. Rendered animal materials and treated manure products have significant amount of essential plant nutrients and carbon. Since organic fertilizer materials have significant amount of carbon, thesecan beutilized for anaerobic soil disinfestation (ASD), which is a technique to manage the aerobic weeds and soil borne pests by creating anaerobic conditions in soil. However, during ASD, rapid nitrogen (N) mineralization from carbon based organic nutrient materials could lead to significant nutrient losses, necessitating measures to modify the N mineralization rate for their dual-purpose use.To regulate the N mineralization, form organic fertilizer materials, three lab incubation studies and one lysimeter (leachate collection) study were conducted. We tested different natural amendments (sulfur) including horticultural oils (neem oil and karanja oil) for their ability to regulate the N mineralization form MBM and DAF solids. Three laboratory incubation studies were conducted under controlled conditions and impact of different natural amendments (NAs) was evaluated on ammonification, nitrification, and net N mineralization form MBM and DAF. The MBM-N mineralized (ammonium + nitrate) at a faster rate than N mineralization from DAF solids. The MBM amended with sulfur at 6% of N significantly increased the soil NH4+-N content at 7, 14 and 21 days after incubation and decreased the soil NO3- -N content. In DAF solids, application of neem oil at 10% of N, significantly lowered the soil NO3- content at 7, 14 and 21 days after incubation than other treatments. The MBM without NAs exhibited the highest net N mineralization (38.11 %), whereas MBM amended with sulfur (at 10% of N) exhibited 27.03% and neem oil (at 10% of N) recorded lowest net N mineralization (15.57%) within first 14 days. Similarly, DAF solids without NAs had the highest (9.07%) net N mineralization rate, on the other hand, DAF with neem oil (at 6% of N) showed the lowest (5.95%) net N mineralization within first 56 days of incubation. DAF solids amended with different NAs had the highest net N mineralized within 56 to 77 days after incubation which was 25.67% as compared to 14.76% in DAF solids without NAs. The DAF solids amended with neem oil (at 10% of N) significantly decreased the net N mineralization (by 12.97%) within first 21 days of incubation. In order to evaluate the form, amount, and the rate at which N is leached below plant root zone, a column leachate study was conducted. The soil in columns was fertilized with different organic fertilizer formulations selected from initial lab incubation studies. A total of 8 treatments were evaluated in leachate study with MBM, DAF, MBM and DAF amended with sulfur and neem oil, ammonium nitrate fertilizer (a positive control) and no fertilizer (negative control) in the column study. Leachate was collected at 7 days interval starting from day 1 after applying the treatments, by leaching with 500 ml of DI water every time. We observed that 1.98 mg and 1.11 mg NH4+ -N was leached from MBM amended with sulfur which was significantly higher than the treatment of MBM alone (1.38 mg and 0.45 mg) at day 7 and day 14, respectively. MBM with sulfur gave the highest NH4+ -N concentration (1.49 mg) in the leachate at day 28 than MBM alone treatment. On the other hand, significantly lower NO3- -N was leached from MBM with sulfur (10.92 mg and 24.42 mg) as compared to MBM alone (17.73 mg and 37.45 mg) at day 7 and day 14, respectively. Similarly, DAF with neem oil (10% of N) had less NO3- -N (13.29 mg) leached than DAF alone (20.44 mg) at day 21. More than 98% of the total N leached was in NO3- form of N with only 1-2 % of total N leached was in NH4+ form of N from different treatments. The leachate was collected up to 56 days after adding the treatments into columns. Ammonium nitrate fertilizer had the highest amount of NO3- -N in the leachate (73.61 mg, 104.45 mg, 127.71 mg, 125.68 mg and 129.56 mg) at day 21, 28, 35, 42 and 56 days after treatment application, respectively. Within first 56 days, only 3.98% and 2.35% of cumulative N (of the total applied N) was lost in the leachate from MBM and DAF, respectively, which was significantly lower than inorganic fertilizer (ammonium nitrate: 26.87% of total N was lost via leaching within first 56 days). The soil from leachate columns (at 56 days after treatment application) was split into three different depths (0-15, 15-30 and 30-45 cm) and analyzed for soil exchangeable ammonium and nitrate content. The MBM amended with S retained significantly more mineralized N in ammoniacal and nitrate form in 0-15, 15-30 and 30-45 cm soil profile in leachate column, as compared MBM alone. Similarly, DAF solids amended with neem oil retained higher soil ammonium N in top 0-15 soil profile as compared DAF alone.
Publications
- Type:
Conference Papers and Presentations
Status:
Published
Year Published:
2024
Citation:
Singh, D., Sanders, T., Jatana, B.S. (2024) Mineralization pattern of different organic nutrient sources as impacted by different natural amendments. 7th Annual Clemson Student Research Forum, Clemson University, Clemson, South Carolina; April 5.
- Type:
Conference Papers and Presentations
Status:
Published
Year Published:
2024
Citation:
Singh, D., Sanders, T., Jatana, B.S. (2024) Optimizing mineralization pattern of organic nutrient sources through natural amendments. College of Agriculture, Forestry and Life Sciences annual Graduate Student Symposium. Piedmont Research and Education Center, Clemson University; Aug. 19-20.
- Type:
Other
Status:
Published
Year Published:
2024
Citation:
Jatana, B.S. (2024) Indoor talk: Organic watermelon research at Edisto Research and Education Center. Watermelon field day at Edisto Research and Education Center, Clemson University; July 11, 2024.
- Type:
Conference Papers and Presentations
Status:
Accepted
Year Published:
2024
Citation:
Jatana, B.S., Sanders, T. (2024) Effect of different natural amendments on mineralization dynamics of different organic nutrient sources. Agronomy Society of America- Soil Science Society of America-Crop Science Society of America Annual meeting, San-Antonio, Texas; Nov. 10-13.
- Type:
Journal Articles
Status:
Submitted
Year Published:
2024
Citation:
Jatana, B.S. (20XX) Short term mineralization dynamics of meat and bone meal as impacted by different natural amendments. Soil Science and Plant Nutrition; Submitted on June 12, 2024.
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