| 000 | 03287nab|a22004577a|4500 | ||
|---|---|---|---|
| 001 | 68754 | ||
| 003 | MX-TxCIM | ||
| 005 | 20251126104803.0 | ||
| 008 | 20251s2025|||||ne ||p|op||||00||0|eng|dd | ||
| 022 | _a1385-1314 | ||
| 022 | _a1573-0867 (Online) | ||
| 024 | 8 | _ahttps://doi.org/10.1007/s10705-025-10399-4 | |
| 040 | _aMX-TxCIM | ||
| 041 | _aeng | ||
| 100 | 1 |
_aOyedele, O. _938717 |
|
| 245 | 1 | 0 | _aMacrofauna accelerates nutrient cycling through litterfall in cocoa agroforestry systems |
| 260 |
_aDordrecht (Netherlands) : _bSpringer Nature, _c2025. |
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| 500 | _aPeer review | ||
| 500 | _aOpen Access | ||
| 520 | _aThis study aimed to better understand nitrogen (N), phosphorus (P), and potassium (K) cycling through litterfall in smallholder cocoa agroforestry systems and to assess if these nutrient flows can be measured using standard litterbags. Annual litter production, relative mass loss, and nutrient loss rates from cocoa leaf litter were evaluated in three farms in south-western Nigeria with and without macrofauna access. Litterfall was measured fortnightly close to the base of the cocoa tree and at the edge of the tree canopies from January 2020 to December 2021. Leaf litter decomposition rates were determined over 388 days in 2 mm mesh litterbags to exclude macrofauna and in frames open to the soil surface to allow macrofauna access. Concentrations of C, N, P, and K were measured in the remaining litter at 180, 244, 314, and 388 days after incubation. Annual estimates of litterfall (10.62 Mg DM ha−1) did not significantly differ between the traps close to and away from the cocoa tree trunk. Nutrient cycling from litter was estimated at approximately 101 kg N, 5 kg P, and 89 kg K ha−1 year−1. Relative litter decomposition rates (k) significantly differed between frames and litterbags. Macrofauna access significantly reduced the C:N ratio in the remaining litter and increased N and P loss from the litter layer by 28 and 69%, respectively. In conclusion, nutrient flows through litterfall are considerable, and N and P transfer rates to soil are likely underestimated in litterbag experiments that exclude macrofauna. | ||
| 546 | _aText in English | ||
| 591 | _aRusinamhodzi, L. : No CIMMYT Affiliation | ||
| 597 |
_dNorwegian Agency for Development Cooperation (Norad) _uhttps://hdl.handle.net/10568/174161 |
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| 650 | 7 |
_aDegradation _2AGROVOC _912234 |
|
| 650 | 7 |
_aFractionation _2AGROVOC _918547 |
|
| 650 | 7 |
_aNutrients _2AGROVOC _91192 |
|
| 650 | 7 |
_aSoil _2AGROVOC _94828 |
|
| 650 | 7 |
_aMacrobenthos _2AGROVOC _938718 |
|
| 650 | 7 |
_aAgroforestry systems _2AGROVOC _96174 |
|
| 700 | 0 |
_aDeo-Gratias Judrita Mawugnon Hougni _8001714252 _gSustainable Agrifood Systems _937564 |
|
| 700 | 1 |
_aHauser, S. _918483 |
|
| 700 | 1 |
_aSchut, A.G.T. _95727 |
|
| 700 | 1 |
_aWoittiez, L.S. _938719 |
|
| 700 | 1 |
_aRusinamhodzi, L. _gSustainable Intensification Program _8CRUL01 _91793 |
|
| 700 | 1 |
_aOgunlade, M.O. _938720 |
|
| 700 | 1 |
_aGiller, K.E. _91960 |
|
| 773 | 0 |
_tNutrient Cycling in Agroecosystems _dDordrecht (Netherlands) : Springer Nature, 2025. _x1385-1314 _gv. 130, p. 427–443 _wu63406 |
|
| 856 | 4 |
_yOpen Access through DSpace _uhttps://hdl.handle.net/10883/35628 |
|
| 942 |
_cJA _n0 _2ddc |
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| 999 |
_c68754 _d68746 |
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