Sustainable intensification of climate-resilient maize-chickpea system in semi-arid tropics through assessing factor productivity.

Global trends show that the rapid increase in maize production is associated more with the expansion of maize growing areas than with rapid increases in yield. This is possible through achieving possible higher productivity through maize production practices intensification to meet the sustainable production. Therefore, a field experiment on "Ecological intensification of climate-resilient maize-chickpea cropping system" was conducted during consecutive three years from 2017-2018 to 2019-2020 at Main Agricultural Research Station, Dharwad, Karnataka, India. Results of three years pooled data revealed that ecological intensification (EI) treatment which comprises of all best management practices resulted in higher grain yield (7560 kg/ha) and stover yield compared to farmers' practice (FP) and all other treatments which were deficit in one or other crop management practices. Similarly, in the succeeding winter season, significantly higher chickpea yield (797 kg/ha) was recorded in EI. Further EI practice recorded significant amount of soil organic carbon, available nitrogen, phosphorus, potassium, zinc, and iron after completion of third cycle of experimentation (0.60%, 235.3 kg/ha,21.0 kg/ha,363.2 kg/ha,0.52 ppm and 5.2 ppm respectively). Soil enzymatic activity was also improved in EI practice over the years and improvement in each year was significant. Lower input energy use was in FP (17,855.2 MJ/ha). Whereas total output energy produced was the highest in EI practice (220,590 MJ ha-1) and lower output energy was recorded in EI-integrated nutrient management (INM) (149,255 MJ/ha). Lower energy productivity was noticed in EI-INM. Lower specific energy was recorded in FP and was followed by EI practice. Whereas higher specific energy was noticed is EI-INM. Each individual year and pooled data showed that EI practice recorded higher net return and benefit-cost ratio. The lower net returns were obtained in EI-integrated weed management (Rs. 51354.7/ha), EI-recommended irrigation management (Rs. 56,015.3/ha), integrated pest management (Rs. 59,569.7/ha) and farmers' practice (Rs. 67,357.7/ha) which were on par with others.

First report of Fusarium verticillioides causing Pokkah boeng disease on maize in India.

Maize is a widely grown cereal crop in India and ranks third to wheat and rice in production (https://iimr.icar.gov.in). During a field survey in Kharif season in 2018, foliar chlorosis at the base and middle of leaves, and twisted top symptoms were observed in 40-50 days old maize plants in Belagavi district, Karnataka, India. Again during Kharif season in 2021, similar symptoms were observed on commercial maize hybrids and sugarcane at Agricultural Research Station, Sankeshwar Karnataka. The symptoms resembled Pokkah boeng disease of sugarcane (Vishwakarma et al. 2013). Symptomatic sugarcane and maize leaves were sampled, surface sterilized with 1.0% sodium hypochlorite, and 70% ethanol, and transferred on Potato dextrose agar, incubated for 10 days at 27±1°C. Fungal growth initiated with white mycelium later turned to pinkish-white with hyaline spores. The morphological features and sporulation patterns of maize and sugarcane samples were similar (e-Xtra 1). Microconidia were formed in long chains and clusters with oval to club-shaped, 0-septate, monophialide-borne microspores. DNA from representative pure culture isolates was extracted using the CTAB protocol (Doyle and Doyle, 1990). The ITS region of r-DNA was amplified with ITS1/ITS4 primers and sequenced. BLAST analyses of sequences of maize and sugarcane culture isolates at NCBI database revealed 100% homology with Fusarium verticillioides MK264336 (Lin et al., 2016). PCR amplification with Fusarium verticilliodes specific primers VER1/VER2 (Mule et al., 2004) confirmed the organism. CBS-KNAW Fungal Biodiversity Centre's Fusarium MLST database also revealed over 98.89% homology with Fusarium verticilliodes (NRRL 46612). The fungal isolates were named Fusarium verticilliodes maize isolate SNK 01 (ON110289) and Fusarium verticilliodes sugarcane isolate SNK 01 (ON564879), and their sequences were deposited in the GenBank. To test pathogenicity, artificial inoculation using maize isolate SNK 01 and cross-inoculation of sugarcane isolate SNK 01 were done on ten maize plants by spraying a conidial suspension (2×106 conidia ml-1) on nonwounded leaves. The plants sprayed with sterile water were used as control. After ten days, typical Pokkah boeng symptoms were observed in the plants inoculated with both maize and sugarcane isolates. Diseased leaves turned pale yellowish-green with small brown spots and a chlorotic appearance, further, these developed into stripes (e-Xtra 2). Wrinkling of leaves was noticed followed by splitting and rotting. No symptoms were noticed in the water-treated control. The pathogens re-isolated from diseased plants inoculated with maize and sugarcane isolates were similar morphologically and identical to the original isolates, fulfilling Koch's postulates. Hitherto, Fusarium verticilliodes was known to cause post-flowering stalk rot in maize. However, this is the first report of Pokkah boeng disease on maize in India caused by F. verticillioides. Considering the economic value of the maize crop, this identification can help develop appropriate disease management strategies to control the disease. References Lee, S. B., et al. 1988. A rapid, high yield mini-prep method for isolation of total genomic DNA from fungi. Fungal Genet. Newsl. 35:23-24. Lin, Z., et al. 2016. Deciphering transcriptomic response of Fusarium verticillioides in relation to nitrogen availability and the development of sugarcane Pokkah boeng disease. Sci. Rep. 6, 29692. Mule, G., et al. 2004. A Species-Specific PCR assay based on the Calmodulin partial gene for identification of Fusarium verticillioides, F. proliferatum and F. subglutinans. European J. Plant Path. 110:495-502 Vishwakarma, S.K., et al. 2013. Pokkah Boeng: an emerging disease of sugarcane. J. Plant Pathol. Microb. 4(3):170. https://iimr.icar.gov.in. Director's desk, ICAR-Indian Institute of Maize Research. (Accessed September 8, 2022).

Productivity, nutrient use efficiency, energetic, and economics of winter maize in south India.

The winter maize area is rapidly spreading in south India in response to rising demand from the poultry and fish feed industries due to the absence of major environmental constraints. Further farmers' are using the winter environment to expand maize area and production. Hence there is immense potential to increase the area under winter maize cultivation. There were no planned field experiments to explore and optimize the right time of sowing and quantity of fertilizer to be added previously due to the presence of negligible winter maize area. Farmers used to cultivate maize as per their choice of sowing time with the application of a quantity of fertilizer recommended for rainy season maize. There were no efforts made towards working on economic analysis including energy budgeting. And hence the investigation was conducted with the objective to explore the optimal planting period and fertilizer levels for winter maize through economic and energy budgeting. Planting windows (1st week of October, 2nd week of October, 3rd week of October, 4th week of October, and 5th week of October) and fertility levels (100 percent recommended dose of fertilizer (RDF), 150 percent RDF, and 200 percent RDF) were used as factors in Factorial Randomized Complete Block Design (RCBD) with three replications. The present investigation revealed that significantly higher winter maize productivity was achieved from the first and second week of October planting along with the application of 200% RDF (recommended dose of fertilizer) followed by 150% RDF. Planting of winter maize during the first week of October recorded significantly higher grain yield (8786kg ha-1) and stover yield (1220 kg ha-1) and was found on par with sowing during the second week of October. Among fertility levels, significantly higher grain yield (8320 kg ha -1) and stover yield (1195 kg ha-1) was recorded with the application of 200% RDF and were found on par with the application of 150% RDF. Further interaction effect showed that higher dry matter production, more days for physiological maturity, higher accumulation of growing degree days, photothermal units, and heliothermal units were recorded from crops planted during the first and second week of October along with the application of either 200% or 150% RDF. However, higher nutrient use efficiency was recorded from the first and second week of October planted crop supplied with lower fertility level (100% RDF). Similarly, significantly higher net returns and gross returns, output energy, net energy, and specific energy were higher from crops planted during the first week of planting along with the application of 200% RDF. Whereas, energy use efficiency and energy productivity were higher with the first week of October planted crop applied with 100% RDF. From the overall interaction, it is recommended to plant winter maize during the first fortnight of October with the application of 150 percent RDF for sustaining higher maize productivity, energy output, and economics in the maize growing area of south India.

Influence of conjunctive use of coffee effluent and fresh water on performance of robusta coffee and soil properties.

A field experiment was conducted to study the influence of treated coffee effluent irrigation on performance of established robusta coffee, nutrient contribution and microbial activities in the soil. The results revealed that the field irrigated with coffee effluent from aerobic tank having COD of 1009 ppm, did not affect the yield of clean coffee (1309 kg/ha) and it was statistically similar (on par) with the plots irrigated with fresh water (1310 kg/ha) with respect to clean coffee yield. Effluent irrigation increased significantly the population bacteria, yeast, fungi, actinomycetes and PSB (122, 52, 12, 34 and 6 x 104/g respectively)) in the soil compared to the soil irrigated with fresh water (87, 22, 5, 24 and 2 x 10(4)/g respectively). The organic carbon (2.60%), available nutrients in the soil like P (57.2 kg/ha), K (401.6 kg/ha, Ca (695.3 ppm), S (5.3 ppm),Cu (4.09 ppm) and Zn(4.78 ppm) were also increased due to effluent irrigation compared to fresh water irrigation. Thus analysis of coffee effluent for major and minor plant nutrients content revealed its potential as source of nutrients and water for plant growth.

Studies on production and characterization of enriched urban waste composts and their influence on crops productivity.

Enriched compost produced with use of municipal solid wastes (MSW) recorded narrow C:N ratio at the end of decomposition period than municipal solid wastes decomposed without enrichers. To enhance the decomposition rate, quality of municipal solid wastes and enrichers/amendments are found very significant for production of compost. Nutrient content particularly nitrogen, phosphorus and potassium could be enhanced with addition of organic amendment/enrichers. Response of different crops for composts produced with addition of different enrichers like night soil, 25% distillery sludge and bio-fertilizers (Azospirillum sp and Bacillus sp) was conspicuous compared to the compost derived from municipal solid wastes alone with respect to increased growth and yield of crops. Among the enriched composts, night soil enriched compost significantly increased the response of potato and groundnut crops. According to farmer's opinion obtained with matrix scoring, chemical fertilizers and sheep penning are cheaper compared to pit compost or urban solid waste compost. While chemical fertilizers are considered to have adverse effects on soil more than pit compost, tank silt, sheep penning and urban solid waste. Weed infestation is associated more with urban waste than other sources. For dry land, agriculture urban waste could be useful due to good moisture holding capacity. Crop yields could be improved under low rainfall condition whenever pit compost or urban solid waste is used.