ライフサイエンスコーパス: agricultural

1 nimal products leading to one of the largest agricultural accidents in U.S. history.

2 hods assess potential long-term impacts from agricultural activities on the production capacity of so

3 Our results reveal that human agricultural activity during the Late Neolithic had alre

4 zed three water quality parameters linked to agricultural and developed land uses (i.e., total dissol

5 There are, however, risks of C leakage if agricultural and forest policies are not aligned leading

6 Our results showed that agricultural and forest streams had comparable N(2) O co

7 ethylene signaling has been manipulated for agricultural and horticultural applications.

8 These designs have been used successfully in agricultural and industrial research and in clinical tri

9 clusters (BGCs), including for compounds of agricultural and medicinal importance, have now been dis

10 ard sustainable phosphorus (P) recovery from agricultural and municipal wastewater streams has intens

11 To better prioritize agricultural and natural systems research, it is crucial

12 Therefore, agricultural and nutritional scientists should harmonize

13 es and cultivars, non-fruit plant parts, and agricultural and processing wastes are underutilized.

14 ites under substantial human use (secondary, agricultural and urban ecosystems) compared with nearby

15 ters phosphorus (P)-rich, eutrophic lakes in agricultural and urbanized watersheds.

16 Underlying agricultural and wetland relationships however were more

17 s in a One Health framework across human and agricultural and wildlife animal health, focusing on the

18 r groundwater resources to fulfill domestic, agricultural, and industrial demands, we face the threat

19 is, low heat treatment, and potential use in agricultural applications.

20 es is a persistent and widespread problem in agricultural areas across Europe.

21 Agricultural areas are considered a particular hotspot f

22 Field surveys in naturally seleniferous agricultural areas in Colorado, United States, found 15-

23 Climate change and conversion of natural or agricultural areas to urban areas will decrease groundwa

24 research is required regarding the impact of agricultural aspects and winemaking techniques on wine o

25 Ultimately, the recent collapse of most agricultural belts and the loss of crop diversity sugges

26 d in conservation programs aiming to protect agricultural biodiversity.

27 mmon with woody biomass residues, carbonated agricultural biomass ash-based monoliths have potential

28 Here, the reactivity of selected agricultural biomass ashes with CO(2) and their ability

29 Three categories of agricultural biomass residues, including shell, fibre an

30 The present work newly focusses on combining agricultural biomass with mineralised CO(2).

31 achieved demonstrate the advantages of using agricultural biotechnology in concert with classical pes

32 ops harbor genetic variants that can advance agricultural biotechnology.

33 s that make chloroplasts valuable targets in agricultural biotechnology.

34 sable tool for plant genetic engineering and agricultural biotechnology.

35 Substantial public health and agricultural burdens remain, despite decades of bats cul

36 -rich biomass, an abundant and underutilized agricultural byproduct.

37 nmental impacts of provisions of fishing and agricultural capital, with and without enforcement of fi

38 ng the groundwater Chloride concentration in agricultural catchments, using the relative variations o

39 s for fertilizer production exacerbates this agricultural challenge.

40 Though the international trade in agricultural commodities is worth more than $1.6 trillio

41 l resolved invasive pest threats in multiple agricultural commodities, ensuring annually accruing (on

42 e future research and resources toward those agricultural communities and water management institutio

43 ity hotspots (p < 0.001) in high-suitability agricultural crop and livestock production areas with re

44 are one of the most important pollinators of agricultural crops and wild plants.

45 Honey produced from agricultural crops differed significantly from all other

46 elipanche, often cause significant damage to agricultural crops.

47 period in wild plants and a shortened one in agricultural crops.

48 ed honey bee colonies is growing slower than agricultural demands for pollination.

49 stently higher (and more variable) levels of agricultural development (2%-37%).

50 ess potential perverse outcomes arising from agricultural development impacting "climate action" (SDG

51 stormwater runoff, wastewater effluent, and agricultural discharge via varying ex situ treatment uni

52 sland for two decades following an intensive agricultural disturbance under ambient and elevated nutr

53 iated pollination is critical for sustaining agricultural economies and biodiversity, yet stands to l

54 production, significantly contributes to the agricultural economies of the Southern Great Plains, USA

55 in China from 1949 to 2012 using an improved agricultural ecosystem model (Dynamic Land Ecosystem Mod

56 ng impacts on the functional biodiversity of agricultural ecosystems.

57 ees are essential for supporting natural and agricultural ecosystems.

58 rsely, loads characteristic of pure urban or agricultural effluents (up to 18 mg N L(-1) week(-1)) le

59 t shallow lakes directly exposed to urban or agricultural effluents.

60 tic cell biology and metabolism, but also to agricultural efforts aimed at improving crop performance

61 imulation model to quantify milk production, agricultural emissions and forest C loss due to grazing.

62 sk of adverse effects of GBHs in natural and agricultural environments.

63 Levant-related ancestry in Africa and early agricultural Europe.

64 Agricultural expansion causes forest degradation in SSA

65 tial are based on coarse assessments of both agricultural extent and aboveground carbon density.

66 ter of human H3N2v cases were reported at an agricultural fair in 2017 in Ohio, where 2010.1 H3N2 IAV

67 017 [sw/OH/2017]) isolated from a pig in the agricultural fair outbreak to replicate in ferrets and t

68 ummer in the United States, youths attending agricultural fairs are exposed to genetically diverse in

69 riant IAV cases reported in association with agricultural fairs.

70 ield group contained fruits that were on the agricultural field over the pre-harvest interval.

71 ion and biodegradation monitoring of PBAT in agricultural field soils.

72 ker amino sugars and SOC, from two long-term agricultural field studies conducted by large United Sta

73 habitat features (river, elephant corridor, agricultural field, trees), and repeated these analyses

74 esticide volatilization rates from a planted agricultural field.

75 In warm regions, agricultural fields are occupied by complex Aspergillus

76 resulted in a record high area of unplanted agricultural fields in the U.S. and especially in the Ma

77 nderstand elephant movement decisions around agricultural fields, and crop consumption.

78 elevant tests of how this diversity modifies agricultural forecasts.

79 vironmental (crops for changing climates and agricultural gene drives).

80 Bird communities in intensive-agricultural habitats proved more susceptible to changes

81 s were evident in intensive- and diversified-agricultural habitats, but were strongest in intensive-a

82 al habitats, but were strongest in intensive-agricultural habitats, where the number of endemic and I

83 rops, especially cereals, can have important agricultural implications.

84 Most traits of agricultural importance are quantitative traits controll

85 table to other insect species of medical and agricultural importance.

86 Root nodules are agricultural-important symbiotic plant-microbe composite

87 lly biases the impact of weather extremes on agricultural income and the potential effects of climate

88 ges in the distribution of climate-dependent agricultural income.

89 Herein, agricultural, industrial, and household chemicals are em

90 Here, we investigate the extent to which agricultural industrialization in the United States was

91 their use in the health, food, cosmetic, and agricultural industries in order to establish knowledge

92 ) and heat-shock promoters from an important agricultural insect pest, Spodoptera frugiperda, is stil

93 herbivore-plant-pollinator networks along an agricultural intensification gradient to explore changes

94 Growing populations and agricultural intensification have led to raised riverine

95 We found that agricultural intensification led to declines in modulari

96 The contribution of agricultural intensification on the deceleration of SCA

97 distributional patterns before and after the agricultural intensification, in the context of land-use

98 capacity for regional food systems based on agricultural land area and productivity, population, and

99 Pasture occupies 70% of agricultural land but contributes <=11% of the domestic

100 cted twenty-first century rapid increases in agricultural land conversion may lead to widespread trop

101 positively associated with the proportion of agricultural land cover around natal sites.

102 ategy, population density, weather, year and agricultural land cover on LDD frequency, LDD distance a

103 chment and mapped to catchments dominated by agricultural land in North and South America and Europe

104 highly suitable for cultivation on ~ 14% of agricultural land in the Czech Republic (8486 km(2)), wh

105 he SOC changes of the soil profile caused by agricultural land use and the correlations with parent m

106 dynamics, and few studies have explored how agricultural land use combined with soil conditions affe

107 However, agricultural land use has a profound impact on SOC dynam

108 was depth dependent and that the effects of agricultural land use on soil profile SOC dynamics varie

109 results indicated that SOC change caused by agricultural land use was depth dependent and that the e

110 along diverse gradients of urbanization and agricultural land use, and identity threshold values bey

111 diversity when converting natural forests to agricultural land use.

112 ation in grasslands, the most common type of agricultural land, to identify under which conditions P

113 Four main sediment sources (agricultural land, unpaved tracks, gullies and channel b

114 val of plant biomass, such as occurs through agricultural land-use change.

115 land surface and include 45% of the world's agricultural land.

116 elligence to locate ground-nests of birds on agricultural land.

117 es in topsoil were observed for all types of agricultural land.

118 Of this, 3700 Mt of plastics are released to agricultural lands and 140 Mt to landscape topsoil.

119 concentrations in this water emanating from agricultural lands are higher than background, and urani

120 mmonly held perception that legacy stores in agricultural lands induce chemostasis where concentratio

121 Erosion management strategies should target agricultural lands with an emphasis on disconnecting unp

122 storage of trees in nonforested portions of agricultural lands.

123 iodiversity-across many taxa and biomes-that agricultural landscapes can support over the short term(

124 mies are often more abundant in fine-grained agricultural landscapes comprising smaller patches and c

125 While improved management of agricultural landscapes is promoted as a promising natur

126 Diversifying agricultural landscapes may mitigate biodiversity declin

127 -prone weeds on field borders and ditches in agricultural landscapes.

128 ant in field margins and ditches surrounding agricultural landscapes.

129 terns, from a hunter-gatherer to a sedentary agricultural lifestyle, which ultimately resulted in the

130 million people worldwide and the associated agricultural losses are estimated at more than US$ 6 bil

131 0%, thus offsetting only a minor fraction of agricultural losses.

132 participants (average age, 62 years) in the Agricultural Lung Health Study, a case-control study of

133 (Campylobacter jejuni) in the most prolific agricultural mammal (cattle).

134 In this work, the effects of agricultural management on the absorption and storage of

135 Here we review the main agricultural management options for increasing SOC stock

136 There are many agricultural management options for increasing soil orga

137 Agricultural management practices influence soil water d

138 Agricultural management practices to enhance soil legacy

139 Agricultural management recommendations based on short-t

140 and these resources are strongly affected by agricultural management.

141 tancing, has been widely reported in Ghana's agricultural markets whereas casual observations and med

142 global estimate of soil NH(3) emissions from agricultural N fertilizer application is constrained.

143 to map the global soil NH(3) emissions from agricultural N fertilizer application.

144 Global agricultural NH(3) emissions from the use of synthetic N

145 nia volatilization (+74%), bringing tropical agricultural nitrate, nitrous oxide, and ammonia losses

146 cing agriculture through increased access to agricultural nutrients.

147 Sodium Dodecyl Sulfate (SDS) in households, agricultural operations, and industries is leading to it

148 cal contamination of water, public areas and agricultural operations.

149 development in wheat and other monocots for agricultural or industrial purposes.

150 ample, the conversion of natural habitats to agricultural or urban ecosystems-is widely recognized to

151 ls, differing in land use history (forested, agricultural, or fallow), with four sterile recipient so

152 coefficients per species group with OECD/FAO Agricultural Outlook and FAO FishStat production volumes

153 To improve agricultural output and sustainability, research should

154 Management of the agricultural pathogen soybean cyst nematode (SCN) relies

155 we investigate methanogenesis in a reflooded agricultural peatland in the Sacramento Delta, Californi

156 h and bridges often disparate ecological and agricultural perspectives for the more experienced.

157 ounds present from commercial, clinical, and agricultural perspectives.

158 ory of exposure to various public health and agricultural pest control insecticides in nature, and th

159 Tetradacus) minax is a major and devastating agricultural pest in Asian subtropical countries.

160 ed Europe and America and has become a major agricultural pest in these areas, thereby prompting inte

161 of Wolbachia-based strategies against major agricultural pests and their transmitted pathogens.

162 e (SIT) has been used to successfully combat agricultural pests at large scale, but not mosquitoes, m

163 manage wild populations of disease vectors, agricultural pests, and invasive species.

164 Locusts are significant agricultural pests.

165 a group of plants with a myriad of academic, agricultural, pharmaceutical, industrial, and social int

166 The role of microbes in sustaining agricultural plant growth has great potential consequenc

167 , leaving them threatened with conversion to agricultural plantations and risking substantial biodive

168 Agrobiodiversity-the variation within agricultural plants, animals, and practices-is often sug

169 rket access for these farmers through online agricultural platforms.

170 Nutrient enrichment from agricultural pollution increases disease pressure in man

171 ble over five generations, demonstrating the agricultural potential of epigenetic variation.

172 ximizing forest cover on soils with marginal agricultural potential while concurrently increasing liv

173 tors involving quality variability (variety, agricultural practice, cold storage, puree mechanical re

174 nding the health conditions, hygiene habits, agricultural practices and the diet of the local inhabit

175 es for AO communities subjected to different agricultural practices and the ways in which this knowle

176 The reuse of sludge as fertilizer in agricultural practices can lead to accumulation of plast

177 vironmental heterogeneity and differences in agricultural practices challenge the practical implement

178 Agricultural practices constitute both the greatest caus

179 'Tulameen' cultivar grown under conventional agricultural practices contained higher anthocyanins lev

180 accumulation in raspberries grown under both agricultural practices in the same edaphoclimatic condit

181 The effect of the agricultural practices on the raspberries' chemical prof

182 ut the impact of organic versus conventional agricultural practices on their phytochemical compositio

183 Agricultural practices strongly affect CH(4) emissions f

184 er the past 50 years, and discussed possible agricultural practices that could increase soil legacy P

185 anthocyanins levels than grown under organic agricultural practices while for the 'Kweli' cultivar no

186 e exploitation of AMF for future sustainable agricultural practices within the context of global clim

187 ound that intensity of land use (grazing and agricultural practices) and dispersal limitation inhibit

188 nd hunger by pursuing sustainable energy and agricultural practices, a third of the food produced aro

189 o two groups: those present in grapes due to agricultural practices, environmental contamination or f

190 72 purees, issued from different varieties, agricultural practices, storage periods and processing c

191 Under organic agricultural practices, the polyphenols levels increased

192 ikely due to different root distribution and agricultural practices.

193 il profile, allowing differentiation between agricultural practices.

194 mpared to the 'Tulameen' cultivar under both agricultural practices.

195 nt differences were observed between the two agricultural practices.

196 kely due to nest failures from predation and agricultural practices.

197 , the main predictors of barrier density are agricultural pressure, density of river-road crossings,

198 diment samples from a Swiss lake under heavy agricultural pressure.

199 for detecting the presence of mold in stored agricultural produce and water-damaged buildings.

200 ical forest than any other, and is a leading agricultural producer.

201 As one of the largest agricultural producers in the world, the European Union

202 South African market was evaluated using the Agricultural Product Standards Act, 1990 as assessment t

203 to assess the likely consequences on future agricultural production and conservation priority areas.

204 facing salinity intrusion, thus challenging agricultural production in these areas.

205 ctions in food waste and postharvest losses, agricultural production must grow to meet future food de

206 increasing problem due to the growth of the agricultural production needed to meet global food deman

207 In the United States, agricultural production requires less irrigated water th

208 in insects, cultivated plants, and water in agricultural production systems.

209 o reduce N(2)O emission from hypoxic soil in agricultural production systems.

210 lting in urban water scarcity, unsustainable agricultural production, and adverse ecological impacts.

211 access, women and girls' education, improved agricultural production, and improved sanitation and chi

212 tegies for simultaneous soil remediation and agricultural production, but a thorough and mechanistic

213 ight could drive unprecedented reductions in agricultural production, endangering global food securit

214 reduce the negative environmental impacts of agricultural production, including soil erosion and nutr

215 e keeping them under the primary function of agricultural production.

216 N fertilizer use and management practices in agricultural production.

217 affect microbial communities and ultimately agricultural productivity in two specific scenarios: fir

218 pread food insecurity persists and increased agricultural productivity will be needed, but much less

219 eatly contributed to substantial increase in agricultural productivity, their over usage has led to b

220 season significantly reduces expected annual agricultural productivity.

221 vigor in natural ecosystems and for reliable agricultural productivity.

222 ity severely reduces plant growth and limits agricultural productivity.

223 al communities are important for maintaining agricultural productivity.

224 onmental threat that limits plant growth and agricultural productivity.

225 me birds reveal that their diet was heavy in agricultural products (namely millet), meaning that they

226 For agricultural purposes or by inadvertent cargo shipment,

227 of crop types that once characterized entire agricultural regions are lost.

228 oduction worldwide, particularly in rain-fed agricultural regions.

229 ase and climate threatens crop productivity, agricultural research develops innovative technologies t

230 idney Diseases, US Department of Agriculture/Agricultural Research Service 58-3092-5-001.

231 l plant systems for research and to increase agricultural resilience and efficiency by developing her

232 ifferent breeding goals during the Neolithic agricultural revolution.

233 However, the long-term ecological effects of agricultural runoff on these populations remains largely

234 versity of field H5N1 Gs/GD viruses from the agricultural sector and assessing cross-protection in a

235 ine development to control H5N1 HPAIV in the agricultural sector and for human prepandemic preparedne

236 /goose/Guangdong/1996 (Gs/GD) lineage in the agricultural sector and some wild birds has led to the e

237 the total N(2) O emissions from the Swedish agricultural sector.

238 vesting capital in local marine fisheries or agricultural sectors achieve income gains for targeted h

239 tural health, industrial, environmental, and agricultural sensing are reviewed.

240 lly replicated, multiyear experiment in four agricultural settings to test if enhancing habitat adjac

241 Beebread from hives in agricultural sites had greater agrochemical diversity an

242 ction following soil disturbance events like agricultural soil fumigation.

243 This reduction is about 29% and 5% of total agricultural soil GHG emissions in China and the world,

244 e accumulation of water-soluble salts in the agricultural soil profile, allowing differentiation betw

245 nvironmental samples, such as pond water and agricultural soil that are susceptible to tetracycline p

246 rley (Hordeum vulgare) genotypes grown in an agricultural soil under controlled environmental conditi

247 Here we report that amending a UK clay-loam agricultural soil with a high loading (10 kg/m(2) ) of r

248 ncept experiment using this technology in an agricultural soil, we simultaneously monitored 84 differ

249 which are produced by many bacteria found in agricultural soils and have well-understood catalytic pr

250 the main source of N available to plants in agricultural soils and in many natural environments.

251 However, agricultural soils are also an important source of nitro

252 t the role of FSa in carbon sequestration in agricultural soils at a global scale may be overlooked.

253 microplastics destined for application on US agricultural soils contained in sewage sludge.

254 e recovery of PBAT added to a total of seven agricultural soils covering a range of physicochemical p

255 (N(2)O) emissions are a matter of concern in agricultural soils especially when flooding (hypoxic con

256 in ~ 33.4 Tg of legacy P accumulated in the agricultural soils from 1967 to 2016, with a current ann

257 Agricultural soils have tremendous potential to sequeste

258 tal sequestration from industrial wastes and agricultural soils is a long-standing challenge.

259 e developed an approach to quantify dsRNA in agricultural soils using quantitative reverse transcript

260 er and sand grains) in solutions relevant to agricultural soils with direct measurements using a surf

261 bility when nanosilver is applied to HA-rich agricultural soils with modest ionic strength.

262 d absolute shortage of mineral P fertilizer, agricultural soils worldwide will be depleted by between

263 In agricultural soils, amino acids can represent vital nitr

264 ilution, degradation, and adsorption) in two agricultural soils.

265 ures on the survival of gammarids in a small agricultural stream.

266 espite higher total N (TN) concentrations in agricultural streams (1,520 +/- 1,640 vs. 780 +/- 600 ug

267 ollected in spring and summer from two small agricultural streams in the drainage basin of Lake Erie,

268 ) O concentrations in forest streams than in agricultural streams is due to the low pH (<6) in forest

269 ces may drive the nutrient dynamics of small agricultural streams that drain to larger rivers and lak

270 nitrogen use efficiency for improved future agricultural sustainability and food security.

271 lies current worldwide cereal yields, future agricultural sustainability demands enhanced nitrogen us

272 ncreasing crop species diversity can enhance agricultural sustainability, but the scale dependency of

273 biome as it relates to both plant health and agricultural sustainability.

274 ate use of insecticides in public health and agricultural system favors an increase in the frequency

275 Soil phosphorus (P) loss from agricultural systems will limit food and feed production

276 Consistently across different forests and agricultural systems, functional richness decreases stee

277 (P) is one of the most limiting nutrients in agricultural systems, P fertilisation is essential to fe

278 rence between current and potential yield of agricultural systems-indicate the ability to increase ou

279 oundation of many ecological communities and agricultural systems.

280 tive demand, is essential for ecological and agricultural systems.

281 incentives to their implementation in global agricultural systems.

282 f of the 20th century due to advancements in agricultural technologies, water management practices an

283 to assess the reactive surface area (RSA) of agricultural top soils.

284 twice the cost of wetland restoration on non-agricultural, undeveloped land-but would provide approxi

285 f course, while dichlorprop was derived from agricultural use more than 30 years ago.

286 of recreational, medicinal, industrial, and agricultural use, and together with its sister genus Hum

287 se of polluting fuels (coal, wood, charcoal, agricultural wastes, animal dung, or kerosene) for house

288 hanisms underlying the adaptation of a major agricultural weed during polyploidization.

289 ives of maize, were recently reported as new agricultural weeds in two European countries, Spain and

290 ty of mechanisms for herbicide resistance in agricultural weeds is helpful for understanding evolutio

291 Worldwide feralization of crop species into agricultural weeds threatens global food security.

292 s created in 2014 to unify all trades in the agricultural wholesale markets of the state to be carrie

293 Agricultural work and occupational pesticide use have be

294 sugarcane industry but not in other forms of agricultural work.

295 n prevalence and risk factors for CKD beyond agricultural workers and in other regions in Nicaragua a

296 ll burden of CKD nationally, with a focus on agricultural workers.

297 s determine carbon uptake, survivorship, and agricultural yield and represent a large proportion of t

298 a focus of plant studies aimed at improving agricultural yield and understanding adaptive processes.

299 ial inoculants for field testing to maximize agricultural yield.

300 ure has documented the effects of weather on agricultural yields.