328 research outputs found

    Modularity of certain products of the Rogers-Ramanujan continued fraction

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    We study the modularity of the functions of the form r(τ)ar(2τ)br(\tau)^ar(2\tau)^b, where aa and bb are integers with (a,b)(0,0)(a,b)\neq (0,0) and r(τ)r(\tau) is the Rogers-Ramanujan continued fraction, which may be considered as companions to the Ramanujan's function k(τ)=r(τ)r(2τ)2k(\tau)=r(\tau)r(2\tau)^2. In particular, we show that under some condition on aa and bb, there are finitely many such functions generating the field of all modular functions on the congruence subgroup Γ1(10)\Gamma_1(10). Furthermore, we establish certain arithmetic properties of the function l(τ)=r(2τ)/r(τ)2l(\tau)=r(2\tau)/r(\tau)^2, which can be used to evaluate these products. We employ the methods of Lee and Park, and some properties of η\eta-quotients and generalized η\eta-quotients to prove our results.Comment: 18 pages, comments welcome. arXiv admin note: text overlap with arXiv:2404.0575

    Analogue of Ramanujan's function k(τ)k(\tau) for the continued fraction of order six

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    The Ramanujan's k(τ)k(\tau) function is defined as k(τ)=r(τ)r(2τ)2k(\tau)=r(\tau)r(2\tau)^2, where r(τ)r(\tau) is the Rogers-Ramanujan continued fraction. Inspired by the recent work of Park (2023) about the analogue of function k(τ)k(\tau) for the Ramanujan cubic continued fraction, we study certain modular and arithmetic properties of the function w(τ)=X(τ)X(3τ)w(\tau) = X(\tau)X(3\tau), where X(τ)X(\tau) is the continued fraction of order six introduced by Vasuki, Bhaskar and Sharath (2010). We consider w(τ)w(\tau) to be an analogue of k(τ)k(\tau) for the continued fraction X(τ)X(\tau)

    Nutrient Cycling in Forage Production Systems

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    In most forage production systems, the nutrients needed for plant growth are provided by microbially mediated breakdown and release of plant-available mineral nutrients from dead plant tissues, livestock excreta, soil organic matter, and geochemically bound mineral forms. Even in fertilized forage systems, determining appropriate fertilizer application rates requires a systems approach on the part of the manager (e.g., Di and Cameron, 2000; Rotz et al., 2002). Fertilizer additions are simply one input in the system of inputs, outputs, pools, and fluxes that characterize nutrient cycling in a particular ecosystem

    Nitrogen and tillage management for corn following alfalfa

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    Rotating alfalfa with corn can increase corn yield potential through improved soil physical properties that enhance water infiltration and root extension, a reduction in disease and pest pressure (i.e., corn rootworm), and an enhanced soil microbial community

    Nitrogen Cycling in Pasture Grazed by Lactating Dairy Cows

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    Increasing use of intensive rotational grazing for livestock production in the USA raises questions about the potential for nitrate-N (NO3- N) leaching losses. In grazing experiments with lactating dairy cows at two sites in the Upper Midwest, we monitored milk production, soil NO3-N concentration, and NO3-N leaching. Dietary supplementation increased milk yield, but there was no measurable impact on NO3-N leaching losses. Leaching volumes and NO3-N losses were small on these silt loam soils, even directly under urine patches. The results suggest that NO3-N leaching is not likely to be a problem on fine-textured soils in the Upper Midwest under pastures dominated by deeply-rooted perennial species, as long as N inputs are moderate and animal management does not degrade the pasture

    Denitrification under Pastures on Permeable Soils Helps Protect Ground Water Quality

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    Pastures have been implicated in ground water contamination by nitrate, especially in humid regions with thin or sandy soils (Stout et al., 2000). Significant losses can occur even under low N input, because available N from excreta patches often exceeds plant uptake capacity. Lack of evidence that appreciable nitrate leaching was occurring in established Midwestern USA pastures led us to test the hypothesis that denitrification was preventing or remediating nitrate loading. Higher denitrification rates have been found in the relatively limited number of trials since Ball & Ryden (1984) first reported the significance of this process in pastures

    Seasonal Distribution of Forage Yield from a Natural Pasture Under Rotational Grazing

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    A 2-yr grazing study was conducted to quantify forage available daily for cattle intake from a natural pasture managed under rotational grazing. Grazing was initiated around 1 May, and was managed with a rotation length of about 17 d each for cycles 1 and 2, and 30 d each for the rest. In 1994, under adequate moisture conditions, forage availability during 5/1-6/1, 6/1-8/15, 8/15-9/15, and 9/15-10/ 15 was 77, 66, 38 and 14 kg DM ha-1 d-1, respectively, resulting in a total yield of 8580 kg ha-1 in 175 d. In 1995, a prolonged period of dry summer reduced the grazing season to 150 d. Forage supply dropped to 46 kg ha-1 d-1 during 6/1-8/15. Natural pastures in northcentral U.S. have the potential to provide significant amount of forage for 5-6 months per year under rotational grazing, but additional feed may be needed for a month or two during periods of stress
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