| Literature DB >> 34285251 |
Rhaony Gonçalves Leite1, Abmael da Silva Cardoso2, Natália Vilas Boas Fonseca1, Maria Luisa Curvelo Silva1, Luís Orlindo Tedeschi3, Lutti Maneck Delevatti1, Ana Cláudia Ruggieri1, Ricardo Andrade Reis1.
Abstract
The effects of nitrogen (pan> class="Chemical">N) fertilization levels on protein and carbohydrate fractions in Marandu palisadegrass pasture [Urochloa brizantha (Hochst. ex A. Rich.) R.D. Webster] were investigated in a pasture over five years. The experimental design was completely randomized with four levels of N (0, 90, 180, and 270 kg N ha-1, as urea) for five years, and with three replicates. The study was conducted in a continuously stocked pasture during the forage growing season (December to April) in a tropical region. The effects of N fertilization were similar across the five years. With increasing N fertilization, the concentrations of crude protein (CP) increased from 103 to 173 g kg-1 (P < 0.001), soluble fractions (Fraction A + B1) increased from 363 to 434 g kg-1 of total CP (P = 0.006); neutral detergent fiber (NDF) decreased from 609 to 556 g kg-1 (P = 0.037); indigestible NDF (P = 0.046), potentially degradable neutral detergent fiber (P = 0.037), and acid detergent fiber decreased (P = 0.05), and total digestible nutrient (TDN) increased (P < 0.001). Increasing N fertilization decreased the concentrations of Fraction C (P = 0.014) and total carbohydrates (P < 0.0001), and increased CP:organic matter digestibility (P < 0.01). Concentrations of neutral detergent fiber free of ash and protein (P = 0.003), indigestible neutral detergent fiber (P < 0.001), neutral detergent fiber potentially degradable (P = 0.11), CP (P < 0.001), Fraction A + B1 (P < 0.001), Fraction B2 (P < 0.001), Fraction B3 (P < 0.01), and non-structural carbohydrates differed (P < 0.001) across years. Therefore, N fertilization can be used to increase CP, soluble protein, and TDN.Entities:
Year: 2021 PMID: 34285251 PMCID: PMC8292324 DOI: 10.1038/s41598-021-94098-4
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
Average chemical composition for Marandu palisadegrass (g kg-1 dry matter) affected by nitrogen dose.
| Variable | Nitrogen dose (kg N ha-1) | Effect1 | |||
|---|---|---|---|---|---|
| 0 | 90 | 180 | 270 | ||
| TC | 783.7 (15.6) | 760.8 (16.0) | 742.1 (15.4) | 721.3 (17.8) | Linear |
| NFC | 94.4 (4.5) | 90.8 (5.2) | 90.1 (6.6) | 85.9 (8.1) | ns |
| apNDF | 609.3 (7.0) | 590.0 (6.9) | 572.0 (5.7) | 556.4 (5.6) | Linear |
| iNDF | 187.8 (2.3) | 177.1 (2.4) | 174.1 (1.8) | 156.5 (1.5) | Linear |
| NDFpd | 421.5 (8.2) | 413.0 (6.7) | 397.9 (7.2) | 399.9 (8.1) | Quadratic |
| ADF | 327.0 (6.5) | 307.0 (6.9) | 301.6 (7.8) | 294.7 (6.5) | Linear |
| Lignin | 87.3 (2.1) | 85.0 (2.4) | 83.3 (2.5) | 86.0 (1.9) | ns |
| TDN | 629.9 (11.4) | 636.0 (10.3) | 638.5 (15.6) | 642.2 (13.4) | Linear |
| CP:DOM (g CP kg-1 DOM) | 125 (7) | 152 (8) | 174 (8) | 195 (10) | Linear |
| CP | 103.2 (10.1) | 128.6 (11.3) | 150.0 (14.4) | 172.8 (14.3) | Linear |
| Fraction A + B1 (g kg-1 CP) | 363.3 (8.2) | 369.0 (7.2) | 406.1 (8.1) | 433.2 (7.2) | Linear |
| Fraction C (g kg-1 CP) | 125.0 (3.5) | 103.7 (2.8) | 101.9 (3.7) | 98.3 (2.9) | Linear |
1Orthogonal polynomial effect of N doses. Effect probability (apNDF, P < 0.0001; iNDF, P = 0.046; NDFpd, P = 0.037; ADF, P = 0.05; Lignin, P = 0.19; TDN, P < 0.0001; TC, P < 0.0001; CP:DOM, P < 0.01; CP, P < 0.001; Fraction A + B1, P = 0.006; and Fraction C, P = 0.014). Within parentheses is the standard error of the means (SEM; ±).
Average chemical composition for Marandu palisadegrass (g kg-1 dry matter) affected by year.
| Variable | Experimental year | Effect1 | ||||
|---|---|---|---|---|---|---|
| 2015 | 2016 | 2017 | 2018 | 2019 | ||
| apNDF | 589.6 (5.4) | 541.3 (5.7) | 605.4 (6.7) | 620.4 (4.9) | 552.9 (4.7) | Cubic |
| iNDF | 116.0 (1.0) | 167.4 (6.0) | 215.4 (7.6) | 204.2 (4.6) | 166.2 (9.6) | Quadratic |
| NDFpd | 473.6 (3.9) | 373.9 (7.1) | 390.0 (5.6) | 416.3 (5.2) | 386.6 (3.4) | ns |
| ADF | 298.2 (2.8) | 254.4 (2.3) | 302.7 (3.1) | 361.5 (3.1) | 312.3 (2.9) | Cubic |
| OM | 911.5 (1.9) | 922.0 (2.3) | 919.0 (2.2) | 911.9 (2.0) | 908.6 (1.9) | Quadratic |
| NFC | 136.3 (10.7) | 246.6 (13.2) | 162.5 (14.2) | 134.2 (9.7) | 170.6 (15.3) | Cubic |
| CP | 123.1 (12.1) | 130.1 (11.6) | 127.5 (9.8) | 142.2 (13.5) | 170.2 (16.5) | Linear |
| Fraction A + B1 (g kg-1 CP) | 325.4 (3.3) | 302.1 (3.6) | 367.9 (4.1) | 382.9 (3.8) | 586.0 (3.2) | Linear |
| Fraction B2 (g kg-1 CP) | 282.5 (2.2) | 245.3 (2.5) | 284.0 (2.8) | 177.8 (2.0) | 166.6 (2.2) | Quadratic |
| Fraction B3 (g kg-1 CP) | 314.0 (3.4) | 340.4 (3.6) | 229.6 (3.7) | 264.5 (2.8) | 196.1 (2.9) | Quadratic |
1Orthogonal polynomial effect of N doses. Effect probability (apNDF, P = 0.003; iNDF, P < 0.001; NDFpd, P = 0.11; ADF, P < 0.0001; NFC, P < 0.001; CP, P < 0.001; Fraction A + B1, P < 0.001; Fraction B2, P < 0.001; and Fraction B3, P < 0.01). Within parentheses is the standard error of the means (SEM; ±).
Figure 1Precipitation, temperature, and sunlight from 2015 to 2019 at the experimental site at the São Paulo State University Jaboticabal, São Paulo, Brazil.
Means soil chemical caracteristcs of the experimental area at the depth of 0 – 20 cm, Jaboticabal– SP.
| Year | P resin | S-SO42- | OM | pH CaCl2 | K+ | Ca2+ | Mg2+ | H+Al | Al3+ | CEC | V% |
|---|---|---|---|---|---|---|---|---|---|---|---|
| – mg/dm3– | g/dm3 | ––mmolc/dm3–– | |||||||||
| 2015 | 12 | 16 | 25 | 5,2 | 2,6 | 36 | 11 | 22 | 0 | 92 | 62 |
| 2016 | 15 | 11 | 27 | 5,1 | 2,8 | 37 | 17 | 28 | 0 | 98 | 61 |
| 2017 | 13 | 12 | 28 | 5,1 | 3,0 | 35 | 14 | 24 | 0 | 95 | 59 |
| 2018 | 12 | 16 | 26 | 5,2 | 3,0 | 34 | 13 | 22 | 0 | 94 | 59 |
| 2019 | 11 | 15 | 28 | 5,2 | 2,9 | 32 | 13 | 23 | 0 | 92 | 57 |
P = phospuros, S-SO42- = sulfate, OM = organic matter, K = potassium, Ca = Calcium, Mg = magnesium, Al = alluminum, CEC = capacity os exchange cations and V% = bases saturation.