28,150 research outputs found
Nutrient Management for Higher Productivity of Swarna Sub1 Under Flash Floods Areas
Two field experiments were conducted at Regional Agricultural Research Station, Tarahara, Nepal during 2012 and 2013 to determine the effect of agronomic management on growth and yield of Swarna Sub1 under flash floods. The first experiment was laid out in a split plot design with three replications; and four different nutrient combinations at nursery as main plots and three age groups of rice seedlings as sub plots. The second experiment was laid out in a randomized complete block design and replicated thrice; with three post flood nutrient doses at six and 12 days after de-submergence (dad). The experiments were complete submerged at 10 days after transplanting for 12 days. The survival percentage, at 21 dad, was significantly higher in plots planted with 35 (90.25%) and 40 (91.58%) days-old seedlings compared to 30 days-old seedlings (81.75%). Plots with 35 days-old seedlings produced 5.15 t ha-1 with advantage of 18.83% over 30 days-old seedlings. Plots with 100-50-50 kg N-P2O5-K2O/ha at nursery recorded the highest grain filling of 79.41% and grain yield of 5.068 t/ha with more benefit. Post flood application of 20-20 N-K20kg/ha at 6 dad resulted in higher plant survival and taller plants, leading to significantly higher grain yield of 5.183 t/ha and straw yield of 5.315 t/ha. Hence, 35-40 days old seedlings raised with 100-50-50 kg N-P2O5-K2O /ha in nursery and the additional application of20-20 kg N-K2O /ha at 6 dad improved plant survival and enhanced yield of Swarna Sub1 under flash flood conditions. The practice has prospects of saving crop loss with getting rice yield above national average yield leading to enhanced food security in the flood prone areas of Nepal
Integrated and ecological nutrient management
This VEGINECO method manual is one of a series of publications resulting from the VEGINECO project. VEGINECO specialises in producing tested and improved multi-objective farming methods for key farming practices – e.g. crop rotation, fertilisation and crop protection – to facilitate the integration of potentially conflicting objectives like economy and ecology. This report describes a methodology for developing nutrient management strategies. In addition, examples of its application under different conditions in Europe are presented
Response of nutrient management practices through organic substances on rice var. GR-11 in North Konkan Coastal zone of Maharashtra
The management of soil organic matter is crucial to maintain a productive organic farming system. No one source of nutrient usually fulfills to maintain productivity and quality control in organic system.In addition, the inputs to supplement nutrient availability are often not uniform presenting additional challenges in meeting the nutrient requirements of crops in organic system.With this concept, a field experiment was conducted at the research farm of ASPEE Agricultural Research and Development Foundation, Tansa Farm, At Nare, Taluka Wada, Dist. Palghar, Maharashtra, during Kharif 2016-17 in rice.Different treatments comprising organic amendments such as Azotobacter, Banana Pseudostem sap 2%, Vermiwash 2% and Panchgavya 2% each applied alone or in all possible combinations were tried in organic crop production.These treatments were compared with absolute control (No biofertilizer+ No Spray). Recommended dose of chemical fertilizer 100:50:50 kg NPK ha-1. A Rice variety ‘GR-11\u27 was taken.Results revealed a significant enhancement in grain yield of rice over absolute control due to the application of different organic amendments applied alone or in combinations. Rice grain yield increased by 35.5% over absolute control when organic amendments viz., Seedling deep in Azotobacter + Vermiwash 2% + Banana Pseudostem Sap 2% were applied together.The rice grain yield (5.7 t ha-1) obtained under combined application of above three organic amendments was at par with the yield recorded under seedling deep in Azotobacter + Vermiwash 2% + Panchgavya 2%.An interesting observation recorded was that there was no serious attack of any insects pest or disease in organically grown crop.The study revealed that addition of four organic amendments viz. seedling deep in Azotobacter, vermiwash 2%, Panchgavya 2% and Banana Pseudostem Sap 2% could give the optimum yield of organic rice var. GR-11
Nutrient management
Vertisols and soils with vertic properties are an important soil group in the Ethiopian highlands. Poor drainage, soil, water and nutrient erosion are the most serious problems on highland Vertisols. Due to their high moisture- storage capacity, they have high production potential and this potential remains underutilised because of the difficulty of managing these soils. This paper summarises available information on chemical properties, N, P and mineralogy. Literature on the P status of soils, P nutrition of forage legumes and crops, mycorrhizae and P nutrition, species and varietal variation in response to P, P sorption isotherms and P fertilisation based on forage-based cropping systems is reviewed. The review also highlights the response of various crops to N in the presence of appropriate rhizobium, microbial studies and biological nitrogen fixation and its cycling in Vertisol cropping
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Nutrient Management
Nutrient elements are required by cranberry plants for the production of vegetation (new leaves and stems), roots, and fruit (crop). Cranberry plants get these nutrients from the soil, from water, or from fertilizers added to the bog. While cranberries require the same nutrients as other plants, they are unique in that the amounts required are much smaller than for most crop plants. The reason for this is that cranberries have adapted through evolution for growth on acid, sandy soils. These soils have little nutrient content, and the plants in the family Ericaceae such as cranberries and blueberries that evolved on them have correspondingly low nutrient needs. Further, cranberries are perennial plants with the capacity to store and reuse nutrients in old leaves, wood, and roots. A unique and important feature of cranberries is that they maintain their leaves over the winter. These leaves also serve as a nutrient source when the plants resume growth in the spring.
Commercially, cranberries are grown in either organic soils modified by surface application of sand, or in mineral soils. The rooting zone typically contains about 95% sand. Average organic matter in the surface horizon of Massachusetts cranberry soils is less than 3.5% and silt and clay make up less than 3% of the soil. Therefore, cranberry soil has low cation exchange capacity - little ability to hold positively charged nutrients such as ammonium, potassium, magnesium, and calcium. However, downward leaching of nutrients is minimized by the layered structure of cranberry bog soil. Layers of sand are added to the bogs every 2-5 years leading to alternating sandy and organic layers. The organic layers are comprised of decaying roots and leaves. Nutrient leaching is also minimized in peat based soils by the high organic matter content of the subsoil.
Why cranberries need fertilizer: Each season nutrients are removed from the bog during harvest and detrashing (removal of fallen leaves from the bog floor). When the fruit is harvested, the elements removed in the largest quantities are nitrogen, potassium, and calcium, at \u3e20 lb/A (nitrogen) or \u3e15 lb/A (potassium and calcium) in an average (150 bbl/A) crop. The amount of nutrient removal increases with increasing crop load and is less when crops are small. It is to compensate for nutrient removal that cranberry growers add fertilizer to their bogs. Most fertilizer added to producing cranberry bogs contains nitrogen, phosphorus, and potassium (N-P-K fertilizer). Phosphorus is included in the mixture to maintain nutrient balance and because much of the phosphorus in cranberry bog soil is not available to the plants at crucial growth stages.
Fertilizer is applied to cranberry bogs using ground rigs (spreaders and seeders), helicopters (aerial application), and the sprinkler system (fertigation)
Evaluation of rice–legume–rice cropping system on grain yield, nutrient uptake, nitrogen fixation, and chemical, physical, and biological properties of soil
To achieve higher yields and better soil quality under rice–legume–rice (RLR) rotation in a rainfed production system, we formulated integrated nutrient management (INM) comprised of Azospirillum (Azo), Rhizobium (Rh), and phosphate-solubilizing bacteria (PSB) with phosphate rock (PR), compost, and muriate of potash (MOP). Performance of bacterial bioinoculants was evaluated by determining grain yield, nitrogenase activity, uptake and balance of N, P, and Zn, changes in water stability and distribution of soil aggregates, soil organic C and pH, fungal/bacterial biomass C ratio, casting activities of earthworms, and bacterial community composition using denaturing gradient gel electrophoresis (DGGE) fingerprinting. The performance comparison was made against the prevailing farmers’ nutrient management practices [N/P2O5/K2O at 40:20:20 kg ha−1 for rice and 20:30:20 kg ha−1 for legume as urea/single super-phosphate/MOP (urea/SSP/MOP)]. Cumulative grain yields of crops increased by 7–16% per RLR rotation and removal of N and P by six crops of 2 years rotation increased significantly (P < 0.05) in bacterial bioinoculants-based INM plots over that in compost alone or urea/SSP/MOP plots. Apparent loss of soil total N and P at 0–15 cm soil depth was minimum and apparent N gain at 15–30 cm depth was maximum in Azo/Rh plus PSB dual INM plots. Zinc uptake by rice crop and diethylenetriaminepentaacetate-extractable Zn content in soil increased significantly (P < 0.05) in bacterial bioinoculants-based INM plots compared to other nutrient management plots. Total organic C content in soil declined at 0–15 cm depth and increased at 15–30 cm depth in all nutrient management plots after a 2-year crop cycle; however, bacterial bioinoculants-based INM plots showed minimum loss and maximum gain of total organic C content in the corresponding soil depths. Water-stable aggregation and distribution of soil aggregates in 53–250- and 250–2,000 μm classes increased significantly (P < 0.05) in bacterial bioinoculants-based INM plots compared to other nutrient management plots. Fungal/bacterial biomass C ratio seems to be a more reliable indicator of C and N dynamics in acidic soils than total microbial biomass C. Compost alone or Azo/Rh plus PSB dual INM plots showed significantly (P < 0.05) higher numbers of earthworms’ casts compared to urea/SSP/MOP alone and bacterial bioinoculants with urea or SSP-applied plots. Hierarchical cluster analysis based on similarity matrix of DGGE profiles revealed changes in bacterial community composition in soils due to differences in nutrient management, and these changes were seen to occur according to the states of C and N dynamics in acidic soil under RLR rotation
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