Knowledge (XXG)

Secondary forest

Source đź“ť

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Rozendaal, Danaë M. A.; Bongers, Frans; Aide, T. Mitchell; Alvarez-Dávila, Esteban; Ascarrunz, Nataly; Balvanera, Patricia; Becknell, Justin M.; Bentos, Tony V.; Brancalion, Pedro H. S.; Cabral, George A. L.; Calvo-Rodriguez, Sofia; Chave, Jerome; César, Ricardo G.; Chazdon, Robin L.; Condit, Richard
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followed by shrubs and bushes. Over time, trees that were characteristic of the original forest begin to dominate the forest again. It typically takes a secondary forest 40 to 100 years to begin to resemble the original old-growth forest; however, in some cases a secondary forest will not succeed,
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When forests are harvested, they either regenerate naturally or artificially (by planting and seeding select tree species). The result is often a second growth forest which is less biodiverse than the old growth forest. Patterns of regeneration in secondary forests show that species richness can
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Deforestation is one of the main causes of anthropogenic carbon dioxide emissions, making it one of the largest contributors to climate change. Though preserving old-growth forests is most effective at maintaining biodiversity and ecosystem functionality, secondary forests may play a role in
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and soil of secondary forests is anticipated to be released into the atmosphere. In other places, forest restoration – namely the development of secondary forests – has been a governmental priority in order to meet national and international targets on biodiversity and carbon emissions.
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Secondary forestation is common in areas where forests have been degraded or destroyed by agriculture or timber harvesting; this includes abandoned pastures or fields that were once forests. Additionally, secondary forestation can be seen in regions where forests have been lost by the
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Low to moderate disturbances have been shown to be extremely beneficial to increase in biodiversity in secondary forests. These secondary disturbances can clear the canopies to encourage lower canopy growth as well as provide habitats for small organisms such as insects, bacteria and
365:. In addition to soil nutrient levels, two areas of concern with tropical secondary forest restoration are plant biodiversity and carbon storage; it has been suggested that it takes longer for a tropical secondary forest to recover its biodiversity levels than its carbon pools. In 227:
and identities of species can take much longer to recover. Artificially restored forests, in particular, are highly unlikely to compare to their old-growth counterparts in species composition. Successful recovery of biodiversity is also dependent upon local conditions, such as
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Leite, Márcio Fernandes Alves; Liu, Binbin; Gómez Cardozo, Ernesto; Silva, Hulda Rocha e; Luz, Ronildson Lima; Muchavisoy, Karol Henry Mavisoy; Moraes, Flávio Henrique Reis; Rousseau, Guillaume Xavier; Kowalchuk, George; Gehring, Christoph; Kuramae, Eiko Eurya (March 2023).
369:, growth of new forests from abandoned farmland exceeded loss of primary rainforest in 1990. However, due to the diminished quality of soil, among other factors, the presence of a significant majority of primary forest species fail to recover in these second-growth forests. 277:. Despite the species loss that occurs with primary forest removal, secondary forests can still be beneficial to ecological and anthropogenic communities. They protect the watershed from further erosion and provide habitat; secondary forests may also buffer 213:
Secondary forests can also be classified by the way in which the original forest was disturbed; examples of these proposed categories include post-extraction secondary forests, rehabilitated secondary forests, and post-abandonment secondary forests.
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systems of agriculture. While many definitions of secondary forests limit the cause of degradation to human activities, other definitions include forests that experienced similar degradation under natural phenomena like fires or landslides.
42:, Canada, is generally considered to have second and third growth characteristics. This photo shows regeneration, a tree growing out of the stump of another tree that was felled in 1962 by the remnants of 313:
have led to efforts to reduce and combat deforestation in places like Panama and Indonesia. Natural and human-assisted growth of secondary forests can offset carbon emissions and help countries meet
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because the dead trees remain to provide nutrients, structure, and water retention after natural disturbances. Secondary forests are notably different from primary forests in their composition and
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The legal definition of what constitutes a secondary forest vary between countries. Some legal systems allows certain degree of subjectivity in assigning a forest as secondary.
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and intentionally planting/seeding native species can be combined with natural regeneration to restore biodiversity more effectively. This has also been shown to improve
158:. Depending on the forest, the development of primary characteristics that mark a successful secondary forest may take anywhere from a century to several millennia. 182: 979: 82:
forest, as well as third-growth forests that result from harvest in second growth forests. Secondary forest regrowing after timber harvest differs from forest
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most of the forests of the United States – especially those in the eastern part of the country – as well as forests of Europe consist of secondary forest.
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layer, whereas primary forests have several. Species composition in the canopy of secondary forests is usually markedly different, as well.
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that favor bacterial communities rather than the fungal communities seen in old-growth forests or naturally regenerated secondary forests.
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and increase connectivity between them. Secondary forests may also be a source of wood and other forest products for rural communities.
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and livelihoods. Some of these techniques are less successful at restoring original plant-soil interactions. In certain cases (as in
1288: 1268: 567:"Microbiome resilience of Amazonian forests: Agroforest divergence to bacteria and secondary forest succession convergence to fungi" 1945: 624: 1042: 1360: 224: 330: 1433: 1243: 1049: 742:"Secondary disturbances of low and moderate severity drive the dynamics of eastern Canadian boreal old-growth forests" 43: 39: 665:
Chazdon, Robin L. (2008-06-13). "Beyond deforestation: restoring forests and ecosystem services on degraded lands".
1757: 1399: 1350: 1035: 102:; however, they may still be helpful in providing habitat for native species, preserving watersheds, and restoring 794:"Soil Carbon Stocks Decrease following Conversion of Secondary Forests to Rubber (Hevea brasiliensis) Plantations" 1720: 1540: 1409: 1070: 274: 1859: 1545: 1153: 1118: 528:"Classification systems for secondary forests in four neotropical countries: Synthesis and conceptual analysis" 233: 236:(resulting from human operations like mining), and management strategies (in assisted restoration scenarios). 2071: 1688: 1579: 1475: 1470: 2081: 1465: 1460: 1328: 1007: 103: 1973: 1959: 1630: 398: 282: 163: 131: 87: 83: 67: 1849: 1589: 1530: 1500: 1370: 1158: 805: 753: 674: 471: 123: 942: 296:
in Asia are expected to rise by millions of hectares by 2050; as such, the carbon stored within the
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which may feed on the decaying plant material. Additionally, forest restoration techniques such as
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allow sunlight to reach the forest floor. An area that has been cleared will first be colonized by
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or agriculture clearing, or equivalently disruptive natural phenomena. It is distinguished from an
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Blécourt, Marleen de; Brumme, Rainer; Xu, Jianchu; Corre, Marife D.; Veldkamp, Edzo (2013-07-19).
78:(primary or primeval forest), which has not recently undergone such disruption, and complex early 2001: 1520: 1515: 1345: 1308: 1263: 1216: 1123: 1113: 925: 920: 293: 232:, water availability, forest size, existing vegetation and seed sources, edge effect stressors, 292:
than other land-uses, such as tree plantations. Land-use conversions from secondary forests to
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Fiamoncini-Pastório, Fábio; Fiorentin-dos-Santos, Kristiana; Luís de-Gasper, André (2023).
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Secondary forests tend to have trees closer spaced than primary forests and contain less
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Parentage analysis of a regenerating palm tree in a tropical second-growth forest
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area which has regenerated through largely natural processes after human-caused
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quickly recover to pre-disturbance levels via secondary succession; however,
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Though not as effective as primary forests, secondary forests store more
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Martin, Philip A.; Newton, Adrian C.; Bullock, James M. (2013-12-22).
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Forest or woodland area which has re-grown after a timber harvest
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Martin, Maxence; Morin, Hubert; Fenton, Nicole J. (2019-12-11).
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than primary forests. Usually, secondary forests have only one
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may be significantly diminished following the removal of
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tropical ecosystems), agroforestry practices have led to
460:"Biodiversity recovery of Neotropical secondary forests" 982:. Ecological Society of America, Ecology 88: 3065-3075. 987:
Biodiversity recovery of Neotropical secondary forests
1812: 1644: 1486: 1177: 1087: 130:Secondary forests re-establish by the process of 1008: 921:"New Jungles Prompt a Debate on Rain Forests" 8: 429:Chokkalingam, U.; de Jong, W. (2001-11-12). 1015: 1001: 993: 897: 835: 817: 765: 600: 582: 545: 499: 303:Intergovernmental Panel on Climate Change 717:"Global Forest Resource Assessment 2020" 329: 181: 410: 357:levels are characteristically low, the 186:Oak plantings in a secondary woodland, 521: 519: 379:Land use, land-use change and forestry 859: 857: 855: 787: 785: 660: 658: 656: 654: 652: 650: 648: 646: 644: 194:and broadleaf woodland is located in 7: 968:. PhD Thesis Wageningen University. 559: 557: 452: 450: 424: 422: 420: 418: 416: 414: 1940: 923:article by Elisabeth Rosenthal in 307:Convention on Biological Diversity 25: 2087:Environmental issues with forests 1289:Global Forest Information Service 2045: 2036: 2035: 2023: 2009: 1995: 1981: 1967: 1953: 1939: 870:Proceedings. Biological Sciences 2046: 547:10.4067/s0717-92002023000300469 1: 966:Dynamics of secondary forests 349:In the case of semi-tropical 989:Science Advances, 2019-03-06 819:10.1371/journal.pone.0069357 122:method, a component of some 40:Vancouver, British Columbia 2103: 1400:Growth and yield modelling 252:functionality, as well as 134:. Openings created in the 1974:Earth sciences portal 1960:Climate change portal 1935: 1541:Great Green Wall (Africa) 1030: 767:10.1007/s13595-019-0891-2 431:"Array - CIFOR Knowledge" 301:Recommendations from the 275:climate change mitigation 268:Climate change mitigation 170:, or 150–500 years. Today 94:, insect infestation, or 1546:Great Green Wall (China) 1119:Close to nature forestry 985:Rozendaal et al., 2019, 953:World Resource Institute 746:Annals of Forest Science 1580:Million Tree Initiative 687:10.1126/science.1155365 283:mature forest fragments 2002:Environment portal 1434:Sustainable management 1329:Trillion Tree Campaign 964:M. van Breugel, 2007, 943:CIFOR Secondary Forest 882:10.1098/rspb.2013.2236 484:10.1126/sciadv.aau3114 346: 199: 47: 1927:Wood process engineer 1631:Urban forest inequity 978:Uzay. 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This mixed 189: 184: 177: 175: 173: 169: 165: 161: 157: 153: 149: 144: 141: 137: 136:forest canopy 133: 128: 125: 121: 112: 110: 107: 105: 101: 97: 93: 89: 85: 81: 77: 73: 69: 65: 61: 57: 53: 45: 44:Typhoon Freda 41: 37: 32: 19: 2021: 2007: 1993: 1979: 1965: 1951: 1944: 1922:Tree planter 1902:Resin tapper 1882:Truck driver 1877:River driver 1626:Tree hugging 1611: 1594: 1561:timber mafia 1551:High grading 1536:Ghost forest 1506:Clearcutting 1429:Silviculture 1405:Horticulture 1313: 1249:Fire ecology 1164:Urban forest 1139:Mycoforestry 1099: 1095:Agroforestry 1076: 1069: 1062: 1055: 1048: 1043:Forest areas 1041: 1034: 948:FAO Forestry 924: 916: 873: 869: 801: 797: 749: 745: 735: 724:. Retrieved 720: 711: 670: 666: 632:. Retrieved 628: 619: 574: 570: 537: 531: 467: 463: 438:. Retrieved 434: 359:soil quality 348: 287: 279:edge effects 271: 246:agroforestry 238: 221: 218:Biodiversity 212: 201: 171: 142: 129: 116: 108: 104:connectivity 100:biodiversity 88:disturbances 68:disturbances 55: 51: 49: 36:Stanley Park 1946:WikiProject 1870:smokejumper 1850:Firefighter 1813:Occupations 1797:Woodworking 1378:Forestation 1309:restoration 1264:informatics 1129:Ecoforestry 721:www.fao.org 389:Overlogging 351:rainforests 326:Rainforests 290:soil carbon 204:undergrowth 196:West Sussex 154:in certain 113:Development 2066:Categories 1892:Lumberjack 1887:Log scaler 1770:engineered 1721:non-timber 1694:sawmilling 1646:Industries 1613:svedjebruk 1324:transition 1304:protection 1294:old-growth 1279:governance 1234:Dendrology 1184:management 1050:Ministries 752:(4): 108. 726:2023-04-02 634:2023-04-02 440:2023-04-02 342:island in 338:canopy on 336:rainforest 334:Secondary 132:succession 70:, such as 1840:Ecologist 1753:Tree farm 1654:Coppicing 1596:chitemene 1496:Acid rain 1444:allometry 1366:SmartWood 1314:secondary 1299:pathology 1274:inventory 1212:driftwood 1078:Arbor Day 890:1471-2954 828:1932-6203 776:1297-966X 695:1095-9203 593:1354-1013 492:2375-2548 96:windthrow 84:regrowing 2041:Category 1855:handcrew 1825:Arborist 1820:Forester 1780:mahogany 1726:palm oil 1716:charcoal 1701:Products 1636:Wildfire 1449:breeding 1410:GM trees 1259:dynamics 1071:Journals 1064:Colleges 1024:Forestry 908:24197410 846:23894456 798:PLOS ONE 703:18556551 611:36511762 602:10108277 510:30854424 384:Land use 373:See also 355:nutrient 344:Thailand 305:(IPCC), 234:toxicity 90:such as 64:woodland 2077:Forests 2051:Outline 1865:lookout 1860:hotshot 1741:tanbark 1711:biomass 1706:biochar 1684:plywood 1669:Logging 1573:wilding 1222:log jam 1179:Ecology 899:3826225 837:3716606 806:Bibcode 754:Bibcode 675:Bibcode 667:Science 501:6402850 472:Bibcode 298:biomass 281:around 192:conifer 162:of the 148:erosion 146:due to 58:) is a 1897:Ranger 1845:Feller 1830:Bucker 1736:rubber 1679:lumber 1489:topics 1476:volume 1471:height 1417:i-Tree 1254:Forest 1207:coarse 1202:Debris 1101:dehesa 972:  906:  896:  888:  844:  834:  826:  774:  701:  693:  609:  599:  591:  533:Bosque 508:  498:  490:  367:Panama 340:Ko Mak 321:Biomes 309:, and 258:Amazon 208:canopy 60:forest 1731:rayon 1466:girth 1461:crown 1422:urban 1319:stand 1227:slash 1217:large 1088:Types 1036:Index 540:(3). 435:CIFOR 405:Notes 311:REDD+ 242:fungi 168:trees 80:seral 1790:teak 1775:fuel 1765:Wood 1585:REDD 1439:Tree 1356:PEFC 1341:ATFS 970:ISBN 904:PMID 886:ISSN 842:PMID 824:ISSN 772:ISSN 699:PMID 691:ISSN 607:PMID 589:ISSN 506:PMID 488:ISSN 92:fire 54:(or 1361:SFI 1351:FSC 1346:CFS 1284:law 1269:IPM 1181:and 894:PMC 878:doi 874:280 832:PMC 814:doi 762:doi 683:doi 671:320 597:PMC 579:doi 542:doi 496:PMC 480:doi 150:or 62:or 2068:: 902:. 892:. 884:. 872:. 868:. 854:^ 840:. 830:. 822:. 812:. 800:. 796:. 784:^ 770:. 760:. 750:76 748:. 744:. 719:. 697:. 689:. 681:. 669:. 643:^ 627:. 605:. 595:. 587:. 575:29 573:. 569:. 556:^ 538:44 536:. 530:. 518:^ 504:. 494:. 486:. 478:. 466:. 462:. 449:^ 433:. 413:^ 317:. 50:A 38:, 1016:e 1009:t 1002:v 910:. 880:: 848:. 816:: 808:: 802:8 778:. 764:: 756:: 729:. 705:. 685:: 677:: 637:. 613:. 581:: 550:. 544:: 512:. 482:: 474:: 468:5 443:. 172:, 143:, 46:. 20:)

Index

Second-growth forest

Stanley Park
Vancouver, British Columbia
Typhoon Freda
forest
woodland
disturbances
timber harvest
old-growth forest
seral
regrowing
disturbances
fire
windthrow
biodiversity
connectivity
slash-and-burn
shifting cultivation
succession
forest canopy
pioneer species
erosion
soil nutrient loss
tropical forests
Hardwood forests
eastern United States
trees

Tilgate Forest

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