| 000 | 040100000a22006370004500 | ||
|---|---|---|---|
| 903 | _aE | ||
| 904 | _aBCO | ||
| 905 | _aC | ||
| 908 | _aJ | ||
| 909 | _aAS | ||
| 912 | _aEn | ||
| 912 | _aEn | ||
| 914 | _aSILVI | ||
| 914 | _aRIBRE | ||
| 914 | _aAG | ||
| 082 | 0 | 4 | _a23031 |
| 100 | 1 |
_966132 _aEwel, J.J. |
|
| 100 | 1 |
_992143 _aMazzarino, M.J. |
|
| 100 | 1 |
_948343 _aBerish, C.W. |
|
| 260 | _c1991 | ||
| 041 | 0 | _aEn | |
| 520 | _aThe fertility of a volcanic-ash derived Inceptisol at a site in the humid tropics of Costa Rica was monitored for five years. Four treatments were established in a randomized block design with six blocks: a sequence of monocultures (two crops of maize (Zea mays) followed by cassava (Manihot esculenta), then the tree species Cordia alliodora), successional vegetation, a mimic of successional vegetation that was physiognomically similar to the model but shared no species with it, and a species-enriched version of successional vegetation. In addition, one plot was maintained free of vegetation. Species-rich successional vegetation was effective at maintaining soil fertility, although general trends of soil-nutrient decline benealth all treatments, presumable because of plant uptake. It proved possible to imitate the fertility-maintaining characteristics of successional vegetation by creating an equally species-rich community of fertility was no enhanced by further species enrichment. Successive peaks of nitrate-nitrogen in soil solution, extractable phosphorus, and extractable potassium occurred during the first year, perhaps driven by an early increment of organic matter from postburn debris and roots. Organic matter, total nitrogen, and extractable sulfur were remarkably stable during the 5-yr period. Depletions of castions, decreases in effective cation exchange capacity (CECe), and increases in acid saturation were related to treatment in the following order: bare soil>monoculture>the three diverse, successional communities. In the bare-soil plot, fertility decreased dramatically: there was a net loss of exchangeable cations and inorganic nitrogen, the phosphorus-fixation capacity increased, and acid saturation reached a potentially toxic 86 percent. At the start of the study, three of the blocks had soil with lower pH, lower CECe, and higher acid saturation. During the study this less fertile soil lost porportionally more cations and increased more in acid saturation and phosphorus-fixation capacity. The less fertile soil under monocultures proved exceptionally vulnerable to loss of fertility; after 5 yr under monocultures, for example, acid saturation reached 38 percent in the more fertile soil and 75 percent in the less fertile soil. In the species-rich communities, however, changes in soil fertility were far less marked. | ||
| 650 | 1 | 4 |
_9165625 _aSUELOS |
| 650 | 1 | 4 |
_9156042 _aNITROGENO |
| 650 | 1 | 4 |
_9147821 _aFERTILIDAD DEL SUELO |
| 650 | 1 | 4 |
_9133936 _aABONOS |
| 650 | 1 | 4 |
_9167494 _aTROPICO HUMEDO |
| 650 | 1 | 4 |
_9148453 _aFOSFORO |
| 650 | 1 | 4 |
_9156299 _aNUTRIMENTOS |
| 650 | 1 | 4 |
_9165551 _aSUCESION NATURAL |
| 650 | 1 | 4 |
_9168904 _aZEA MAYS |
| 650 | 1 | 4 |
_9153830 _aMANIHOT |
| 650 | 1 | 4 |
_9142337 _aCORDIA ALLIODORA |
| 650 | 1 | 4 |
_92064 _aCOSTA RICA |
| 691 |
_9156032 _aNITROGEN |
||
| 691 |
_9165093 _aSOIL FERTILITY |
||
| 691 |
_9147879 _aFERTILIZERS |
||
| 691 |
_9158339 _aPHOSPHORUS |
||
| 691 |
_9168904 _aZEA MAYS |
||
| 691 |
_9153830 _aMANIHOT |
||
| 691 |
_9142337 _aCORDIA ALLIODORA |
||
| 691 |
_aCOSTA RICA _92064 |
||
| 692 | _aAZOTE | ||
| 692 | _aFERTILITE DU SOL | ||
| 692 | _aENGRAIS | ||
| 692 | _aPHOSPHORE | ||
| 692 | _aZEA MAYS | ||
| 692 | _aMANIHOT | ||
| 692 | _aCORDIA ALLIODORA | ||
| 692 | _aCOSTA RICA | ||
| 773 | 0 |
_tEcological Applications (FAO) _d1991 _gv.1(3) p.289-302 |
|
| 040 |
_aCR-TuBCO _cCR-TuBCO _bEs |
||
| 245 | 1 | 0 | _aTropical soil fertility changes under monocultures and successional communities of different structure |
| 942 | _cANA | ||
| 003 | CR-TuBCO | ||
| 999 |
_c51678 _d51678 |
||