ライフサイエンスコーパス: plantation

1 ganic C (SOC) content, compared to the cedar plantation.

2 ) and adjacent bamboo (Phyllostachys edulis) plantation.

3 t cutting and upland grazing prior to forest plantation.

4 verstory-was the main water consumer in this plantation.

5 natural forest and (b) an Acacia crassicarpa plantation.

6 e significantly higher in forest than rubber plantation.

7 e been significantly logged and converted to plantation.

8 s were significantly more abundant in rubber plantation.

9 swamp forest was as old as from the oil palm plantation.

10 e ranging from old growth forest to oil palm plantation.

11 asca vitis (Gothe) (Hemiptera), in a Chinese plantation.

12 forests remaining within Indonesian oil palm plantations.

13 lders to reproductive modification in forest plantations.

14 ne flow into Ireland, and reflect the Ulster Plantations.

15 mitigation when such forests are replaced by plantations.

16 ne of the most dominant pests in Chinese tea plantations.

17 y biomass production in temperate agroforest plantations.

18 , agroforestry, timber plantations, fuelwood plantations.

19 ic structure of E.(M.) onukii in Chinese tea plantations.

20 (SEA) has encouraged the expansion of rubber plantations.

21 ged land uses, including oil palm and timber plantations.

22 obal nature of pest invasions in forests and plantations.

23 ts the productivity of orchards and forestry plantations.

24 d recruits, growing inside and invading from plantations.

25 r borer-predator abundances on more forested plantations.

26 ears of data from two adjacent loblolly pine plantations.

27 iodiversity and ecosystem functioning within plantations.

28 change to smallholder agriculture and forest plantations.

29 cross the study area, especially in oil palm plantations.

30 nd proximity to forest on habitat use within plantations.

31 n shade plantations of C. canephora than sun plantations.

32 jor decrease in diversity with conversion to plantations.

33 around twice as high as those of the Acacia plantation (4.7 +/- 1.5 g CH(4) m(-2) year(-1) ).

34 dynamic structures of a mixed native species plantation, a conifer plantation and an Acacia mangium p

35 e invasion of bamboo into the Japanese cedar plantation accelerated the degradation of SOM.

36 onversion from peat swamp forest to oil palm plantation, accounting for CH(4) and N(2)O as well as CO

37 arby native forests in a region of extensive plantation activity in south-central Chile.

38 ggest that pregnant women living near banana plantations aerially sprayed with mancozeb may be enviro

39 cupancy framework, we evaluated how oil palm plantations affect the occurrence and habitat use of ter

40 sites were counterbalanced by the effect of plantation age, as plantations increased their SOC stock

41 as plantations increased their SOC stocks as plantations aged.

42 aggressively affected by oil palm and cacao plantations, agricultural and urban expansions or illega

43 d scale, process-based studies on how forest plantations alter the partitioning of rainwater and affe

44 Coffee plantations, although lacking most of the forest special

45 a mixed native species plantation, a conifer plantation and an Acacia mangium plantation in Southern

46 and roots) over 18 months in a Sitka spruce plantation and directly compared the fate of this (15) N

47 limantan, Indonesian Borneo, and an oil palm plantation and natural forest in Sarawak, Malaysian Born

48 , a significant (p<0.05) interaction between plantation and season was observed for phenolic constitu

49 itats within the past 35 years by deliberate plantation and seeds floating on the tide.

50 +/- 0.1 for oil palm and cacao agroforestry plantations and 0.8 +/- 0.3 for rubber plantations in th

51 n-destructive inventories across alternative plantations and age classes on peat would further streng

52 We collected 2655 spiders from plantations and established relative abundances of spide

53 t does not distinguish tropical forests from plantations and even herbaceous crops, which leads to a

54 hieved through increasing yields in existing plantations and expansion of new plantations into areas

55 osquitoes were sampled in human settlements, plantations and forest edges, and screened for Plasmodiu

56 that allowing undergrowth vegetation inside plantations and maintaining nearby riparian corridors wo

57 rants, with low acquired immunity, active on plantations and mines, represented a fundamentally diffe

58 eters were measured from three thorny bamboo plantations and nearby bare lands.

59 Plantations and restored forests can improve ecosystem s

60 m threatened with conversion to agricultural plantations and risking substantial biodiversity and car

61 m intensely cultivated lands to high-biomass plantations and some other types of agroforestry.

62 We investigated the location of oil palm plantations and the other major crop - rubber plantation

63 This approach allows for studying desert plantations and the process chain leading to climate mod

64 controlling lepidopteran pests of eucalyptus plantations and those selective to natural enemies, such

65 archaeological investigations of mercantile, plantation, and missionary colonies, this Perspective sh

66 from four near-natural communities and four plantations, and 2) fossil pollen from soil profiles (0-

67 ncessions") for oil palm plantations, timber plantations, and logging activity on primary forests and

68 properties between non-native Pinus radiata plantations, and nearby native forests in a region of ex

69 s coveted by humans, primed for agriculture, plantations, and settlements that nearly always trump co

70 contributors to the eco-exergy stored in the plantations, and thus, the introduction of suitable indi

71 Global croplands, pastures, plantations, and urban areas have expanded in recent dec

72 cover loss in certified and RSPO member-held plantations appear necessary if the RSPO is to yield con

73 of RSPO-certified and noncertified oil palm plantations ( approximately 188,000 km(2)) in Indonesia,

74 Industrial agricultural plantations are a rapidly increasing yet largely unmeasu

75 Oil palm plantations are an iconic symbol of tropical peatland de

76 ting on former agricultural land, and forest plantations are being established for commercial and res

77 ction vary, forests neighboring agricultural plantations are consistently vulnerable to long-lasting

78 Fungi that were frequently detected far from plantations are often found in early-successional sites

79 The date palm plantations are prone to Dubas bug (DB; Ommatissus lybic

80 Migrant workers may introduce pathogens into plantation areas, most worryingly artemisinin-resistant

81 in high quantities with the establishment of plantations around the lakes.

82 o-exergy increased over 3 times in all three plantations, as predicted by the maximum eco-exergy prin

83 of colonies were set in a Eucalyptus grandis plantation at the beginning of the flowering period (aut

84 r in fine roots in a Liquidambar styraciflua plantation at the conclusion of a free-air CO(2) enrichm

85 onse of understory vegetation in Pinus taeda plantation at the Duke Forest FACE site after 15-17 year

86 ical rainforest fragments and derived rubber plantations at a network of sites in Xishuangbanna, Chin

87 heast Asia and sub-Saharan Africa for rubber plantations between 2003 and 2017 [1, 2].

88 ies are used to upscale AGB estimates to the plantation block-level.

89 n this landscape mosaic of native forest and plantations, both soil invertebrate communities and phys

90 peatlands had been drained and converted to plantations by 2010, and much of the remaining forest ha

91 enerated additional genetic gains for forest plantations by selecting more superior genotypes from th

92 losses in drainage water from coastal forest plantations can constrain the long term sustainability o

93 Large-scale sustainable desert agroforestry plantations can contribute to climate change mitigation

94 Plantations can help control groundwater recharge and up

95 , suggesting that fuel conditions in conifer plantations can increase fire severity despite removal o

96 soprene emissions from poplar (Populus spp.) plantations can influence atmospheric chemistry and regi

97 tion for the establishment of tree cash crop plantations causes significant alterations to soil organ

98 eing replaced by rubber (Hevea brasiliensis) plantations, causing widespread concern of a crash in bi

99 vely associated with living within 50 m of a plantation (% change = 42.1; 95% CI: 14.2 to 76.9) and M

100 om two harvesting seasons from four highland plantations), collected from the main tea-growing region

101 or example, 13% of land area is now oil palm plantation, compared with 1% in 1974.

102 55 at prices $35-$100/tCO(2), with intensive plantations comprising <7% of this increase.

103 use categories (protected areas, logging and plantation concessions) is a necessary foundation to pri

104 urs in largely undeveloped oil palm and tree plantation concessions, respectively.

105 tual of 9.8 to 6.6% y(-1) Nevertheless, most plantations contained little residual forest when they r

106 thermore, intensive management in the bamboo plantation could enhance the humification as well.

107 eland subject to different extents of forest plantation cover (4-64% of catchment area).

108 Our results show that rubber plantations cover much larger areas than oil palm in the

109 Oil palm, a plantation crop of major economic importance in Southeas

110 Control samples were obtained from papaya plantations cultivated in experimental areas, in which n

111 not account for temporal variation over the plantation cycle and only consider CO(2) emissions.

112 Our study showed that deforestation for tree plantations decreased SOC stocks by up to 50%.

113 Plantations decreased stream flow by 227 millimeters per

114 cies characteristics are key information for plantation design and forest management, field studies o

115 To avoid this potential decline plantation development in orang-utan habitats must be ha

116 Here, we evaluate impacts of oil palm plantation development on land cover, carbon flux, and a

117 Soil biotic and abiotic characteristics of plantations differed significantly from native forests i

118 Although monoculture plantations dominate existing commitments to restore for

119 southern China, where subtropical coniferous plantations dominate.

120 iffered significantly from native forests in plantation-dominated south-central Chile, with profound

121 ngly dependent on the location of the poplar plantations, due to the prevailing meteorology, the popu

122 90% to total (15) N tracer uptake among four plantations during the study period.

123 erage, twice as high as those in smallholder plantations, ecological indicators displayed substantial

124 re said to have influenced emerging colonial plantation economies in the Americas(1,2).

125 At the plantation edge, affiliation even increased compared to

126 Black tea from low plantation elevation contained 22-28% more polyphenols t

127 to factors including geographical locations, plantation elevations and leaf grades have been limited.

128 We found that both the swamp forest and the plantation emit centuries-old CO(2) from their drainage

129 We demonstrate that large-scale plantations enhance regional clouds and rainfall and der

130 d woody biomass production in the agroforest plantation environment, even in areas with high levels o

131 picture data is acquired from laboratory and plantation environments, the developed vision method wil

132 In unique experimental 16-y-old plantations established in abandoned pasture in lowland

133 rveys, we assess previous and project future plantation expansion under five scenarios.

134 y elevated [CO(2)] in a closed-canopy forest plantation, exposed using a free air CO(2) enrichment te

135 nted teas from six high-, mid- and low-grown plantations; fermented and unfermented teas from two har

136 2375 patients from a dermatologic clinic in Plantation, Florida.

137 the full water cycle in a typical multilayer plantation forest composed of black locust, one of the m

138 verall, changes in land use across native to plantation forest edges differentially affected phylogen

139 human land uses (e.g., tillage agriculture, plantation forestry).

140 sibility of improving valuable genotypes for plantation forestry, a field where in vitro recalcitranc

141 trial raw material has led to development of plantation forestry, in which trees are planted, managed

142 hanges reflect the expansion of fast-growing plantation forests that contribute to timber exports and

143 Moreover, this signal was stronger in plantation forests, indicating that this habitat may imp

144 e across an edge gradient between native and plantation forests.

145 separated the population that originated by plantation from populations that originated naturally by

146 rench West Indies to fight weevils in banana plantations from 1973 to 1993.

147 d plant carbon ('fast' energy channeling) in plantations from the detrital C pathway ('slow' energy c

148 logging, clear-cutting, agroforestry, timber plantations, fuelwood plantations.

149 nd eco-exergy to empower ratios of the three plantations generally increased during the study period,

150 re had the highest DON, and 10-mixed species plantation had the highest DOC.

151 Expansion of oil palm plantations has led to extensive wildlife habitat conver

152 els of isoprene, proliferation of agriforest plantations has significant potential to increase region

153 and superior wood properties, eucalypt tree plantations have emerged as key renewable feedstocks (ov

154 Since mixed plantations have good performance in increasing soil DOC

155 nese fir, we show by direct measurement that plantations have significantly accelerated SOC turnover

156 % used both habitats, indicating that coffee plantations have some conservation value.

157 rainfall and derive an index for predicting plantation impacts.

158 imate for a typical commercial loblolly pine plantation in North Carolina, USA, spanning the entire r

159 btropical tree species in a Pinus massoniana plantation in southern China and found that the chemical

160 , a conifer plantation and an Acacia mangium plantation in Southern China were quantified over a peri

161 t in native forest remnants and shade coffee plantations in a mega-diverse region.

162 Biomass production over 4 y in plantations in Arizona and Oregon was similar among gene

163 The risk to Eucalyptus plantations in Australia is further compounded by planti

164 nt fungal diseases affecting Eucalyptus spp. plantations in Brazil.

165 to end the conversion of natural forests to plantations in Chile at the start of the 21st century.

166 rests, with compositionally simpler, younger plantations in drier regions performing particularly poo

167 ustained conversion of mangroves to oil palm plantations in Malaysia and Indonesia, are identified as

168 using measurements and models, that oil palm plantations in Malaysia directly emit more oxides of nit

169 ially for trapping O. rhinoceros in oil palm plantations in Southeast Asia, and tested against O. mon

170 uring field surveys in commercial eucalyptus plantations in southern Brazil to be examined and dissec

171 lantations and the other major crop - rubber plantations in southern Myanmar, and compared them to co

172 estry plantations and 0.8 +/- 0.3 for rubber plantations in the humid tropics; and (ii) land use mana

173 thogen has had a devastating impact on larch plantations in the United Kingdom as well as mixed conif

174 34 children aged 6-60 mo living on rural tea plantations in West Java, Indonesia, participated in a 3

175 ld-growth forest, logged forest and oil palm plantations) in Borneo.

176 In contrast, tree plantations increased SOC stocks in arid sites but decre

177 balanced by the effect of plantation age, as plantations increased their SOC stocks as plantations ag

178 e ECM fungal community predominated far from plantations, indicating differences between highly invas

179 ts, though phylogenetic evenness declined in plantation interiors.

180 in existing plantations and expansion of new plantations into areas that have already been deforested

181 xpansion of oil palm (OP, Elaeis guineensis) plantations into tropical forest peatlands has resulted

182 lthough the contribution from the non-native plantation is currently low, it is likely that this will

183 However, gene flow from GE forest plantations is a large source of ecological, social and

184 ent of native vegetation by pastures or tree plantations is increasing worldwide.

185 The replacement of native forests by tree plantations is increasingly common globally, especially

186 The global expansion of tree plantations is often claimed to have positive effects fo

187 Plantation land sources exhibited distinctive temporal d

188 cantly over rainforest and adjacent oil palm plantation landscapes.

189 ine due to crop failure, diseases and ageing plantations, leading to price fluctuations and the neces

190 ndary broad-leaved forests and/or coniferous plantations, leading to the land cover changes that alte

191 Plantation leases reveal vast development potential.

192 s) contents were significantly influenced by plantation location.

193 al pattern in CH(4) exchange over the Acacia plantation may be the result of the GWL being consistent

194 ollination probability was highest over pine plantation, moderate over low-intensity agriculture and

195 s, and treatment with rituximab in posttrans-plantation multicentric Castleman disease patients and n

196 ks from paired forests (n = 32) and adjacent plantations (n = 54).

197 Climate impacts from plantations need to be well understood before considerin

198 anther filament length were larger in shade plantations of C. arabica.

199 llen total nitrogen content greater in shade plantations of C. canephora than sun plantations.

200 nitrogen content was lower in sun than shade plantations of C. canephora, but no difference was found

201 xplained by anthropogenic food subsidies via plantations of cash crops, potentially coupled with huma

202 rder analytical model aimed at assessing how plantations of different ages may regulate the persisten

203 months and the remainder within 5 years, but plantations of Eucalyptus were less resilient.

204 change, using well-documented 20(th) Century plantations of exotic conifers as an experimental system

205 Here, we examine how forestry plantations of exotic trees affect critical soil functio

206 To counteract this decline, plantations of native species, often based on non-Britis

207 y relative to native semi-natural forests or plantations of native tree species remain incompletely u

208 of coffee samples into their countries, and plantations of origin was achieved.

209 The productivity of such plantations often exceeds that of less-intensively-manag

210 We quantify the AGB stocks of an OP plantation on drained peat in Malaysia from 3 to 12 year

211 -US$310 ha-year(-1) in damage, a benefit per plantation on par with the average annual income of a Co

212 I was born on a sugar plantation on the island of Hawaii and early on had a st

213 The effects of season and plantation on the polyphenol content of Camellia sinensi

214 tions remain unanswered about the impacts of plantations on belowground diversity and soil properties

215 pulp production, the effects of these exotic plantations on biodiversity relative to native semi-natu

216 s), and cacao (Theobroma cacao) agroforestry plantations on SOC stocks within 3-m depth in deeply wea

217 s had access to the pollen available in this plantation, one was supplemented with a polyfloral polle

218 characteristics of the new vegetation (tree plantations or pastures), its age, and precipitation.

219 tes in four 40-yr-old monoculture coniferous plantations (Pinus koraiensis, Pinus sylvestris, Picea k

220 C I and SEC II), and Cunninghamia lanceolata plantation (PLF).

221 a hardwood deciduous forest (HW) and a pine plantation (PP) co-located in North Carolina, USA, we sh

222 ted, short rotation and fast-growing biomass plantations produced low GWPbio.

223 gineering (GE) can be used to improve forest plantation productivity and tolerance of biotic and abio

224 Hybrid-poplar tree plantations provide a source for biofuel and biomass, bu

225 Mature plantations provide ideal habitats for the mosquito vect

226 act as biological pest control by feeding on plantation rats, the major pest for oil palm crops, with

227 trees for short-rotation forestry or energy plantations, reclamation, phytoremediation, or other app

228 Conversion of tropical forests into oil palm plantations reduces the habitats of many species, includ

229 abitat (native forest vs. shade-grown coffee plantations) relates to spring departure date and migrat

230 f certification on deforestation in oil palm plantations remains unclear.

231 sputed is whether the proliferation of young plantations replacing old forest in the southern United

232 Thus, desert plantations represent a unique environmental solution vi

233 it appears that forest replacement by rubber plantation results in an overall loss and extensive repl

234 Conversion of logged forest into oil palm plantation results in the collapse of most energetic pat

235 Summary data across a range of plantations reveal an average rate of carbon storage an

236 species between 1999 and 2010 in sun coffee plantations, riparian corridors, secondary forests, fore

237 effects of transgenes, transgenic fertility, plantation rotation length, disturbance regime, and spat

238 sed by warmer soil before the closure of the plantation's canopy.

239 Regional modeling of U.S. plantation scenarios suggests that climate feedbacks are

240 an slum communities and 9.02% (4.29-18.0) in plantation sector communities.

241 Further growth of the plantation sector should be achieved through increasing

242 inth infections living in urban slums and in plantation-sector communities.

243 Especially, oil palm plantations seem to negatively affect dispersal in T. lo

244 iodiversity, we recommend that mixed species plantations should be used as a sustainable approach for

245 st pronounced in the topsoil, although older plantations showed considerable SOC losses below 1-m dep

246 rooibos plants (n=54), sampled at commercial plantations, showed that PPAG is not ubiquitously presen

247 onal diversity of soil invertebrates in pine plantation sites.

248 vegetative dispersal was highly dependent on plantation size.

249 which stimulates coffee flowering across all plantations), soil pH, and nitrogen availability.

250 different climate zones, land use types, and plantation species following afforestation.

251 n the native range are rarely found far from plantations, suggesting a means for predicting potential

252 lysable C to total organic C ratio at bamboo plantations supported the hypothesis that decomposition

253 focused not on how to develop drainage-based plantations sustainably, but on whether the sustainable

254 ould be technically feasible in a variety of plantation taxa.

255 re efficiently by microbes colonizing bamboo plantations than in bare land soils.

256 lower litter-calibrated Delta(13)C values in plantations than in rainforests, suggesting that they sw

257 systems such as restored grasslands or tree plantations, the clear lack of any general tendency for

258 with >50% of their catchment area covered by plantations, there were two- to sixfold increases in pig

259 threatening rubber tree (Hevea brasiliensis) plantations throughout South and Southeast Asia and West

260 w license areas ("concessions") for oil palm plantations, timber plantations, and logging activity on

261 in a Malaysian swamp forest and an oil palm plantation to understand how clear-felling, drainage, an

262 The close proximity of rubber plantations to natural forest also increases the threat

263 s or 44 million hectares would be needed for plantations to reach the target of approximately 0.16 Pg

264 ganic carbon in agricultural soils and using plantations to sequester carbon in soils and wood.

265 to drought could allow for the expansion of plantations to sub-prime regions.

266 and diversity decreased from forest edge, to plantation, to human settlement.

267 ntial declines in total P may drive tropical plantations toward greater P limitation as the capacity

268 assy systems for carbon gain using flammable plantation trees could shift the fire regime from lower

269 rate how subsidies from neighboring oil palm plantations triggered powerful secondary 'cascading' eff

270 w that growth of an intact Populus deltoides plantation under increased CO2 (800 micromol x mol(-1) a

271 uct social cost-benefit analyses of oil palm plantations under different scenarios for clearing land

272 clearance for farming and monoculture forest plantations, unsustainable selective logging, overhuntin

273 ested 1,339 samples maintained in Sime Darby Plantation using both mutations.

274 We find that clearing for oil palm plantations using mechanical methods generates higher so

275 We measured gene flow from hybrid poplar plantations using morphological and genetic markers, and

276 9 +/- 0.95 Mg ha(-1) yr(-1) when a 'perfect' plantation was modelled.

277 y variable that predicted SOC changes across plantations was the amount of SOC present in the forest

278 In a Mexican coffee plantation, we excluded foliage-gleaning bird and bat pr

279 orey shrub species in subtropical coniferous plantations, we investigated associations between the ma

280 ies in seasonally dry subtropical coniferous plantations, we investigated contributions of the degree

281 ually converted to productive uses, oil palm plantations were by far the most common outcome.

282 eotropical centre of origin since commercial plantations were first established.

283 ineralization rates of 10-mixed and 30-mixed plantations were similar as that of N-fixing monoculture

284 a 25-yr-old longleaf pine (Pinus palustris) plantation where C flow was manipulated by foliar scorch

285 sed by 200 microliters per liter in a forest plantation, where competition between organisms, resourc

286 er-conservation value grasslands to a timber plantation, while conserving higher-value grasslands for

287 Most species use secondary forests and tree plantations, while only few use human settlements.

288 yanin but were absent from refined sugar and plantation white sugar due to the refining process.

289 The anthocyanin content in refined sugar, plantation white sugar, soft brown sugar and raw sugar w

290 l peat swamp forest conversion into oil palm plantation with periodic burning was 1400 Mg C ha(-1) ov

291 d from 449 pregnant women living near banana plantations with extensive aerial spraying of Mn-contain

292 ltivars, which are usually produced in large plantations with fixed infrastructures and high inputs o

293 Coffee plantations with higher tree cover (7% vs. 13%) had more

294 of heathland areas within commercial conifer plantations with regards to their future management.

295 rbon sequestration strategies highlight tree plantations without considering their full environmental

296 al AR increases the carbon stock of standing plantations, wood products, and biochar, but the increas

297 f age [51% cohabited with one or more flower plantation workers (mean duration, 5.2 years)].

298 se infection on banana is devastating banana plantations worldwide.

299 st, one of the most popular tree species for plantations worldwide.

300 heat stress is a key factor affecting forest plantation yields.