ライフサイエンスコーパス: fertilizer

1 ials in enhancing release of phosphorus from fertilizer.

2 w) and P (1.5% P w/w) can be used as mineral fertilizer.

3 ith increasing application rates of silicate fertilizer.

4 ential nutrient that is a major component of fertilizer.

5 atural nanoclay (attapulgite) to traditional fertilizer.

6 nt bacteria than soil treated with inorganic fertilizer.

7 of farmers who can't -or won't- use nitrogen fertilizer.

8 spectively, without any increase in nitrogen fertilizer.

9 timately used for broadcast application as a fertilizer.

10 such as agricultural loading with artificial fertilizer.

11 te, animal feed, nutritional supplements and fertilizer.

12 ctly to soils as an effective slow-release P-fertilizer.

13 pumpkin fruits decreased with increasing NPK fertilizer.

14 products, such as animal feed, fish meal and fertilizer.

15 alternative technologies, such as phosphite fertilizer.

16 e thus enriched biomass may serve as organic fertilizer.

17 , industrial products, and 4 x 10(9) kg of N fertilizer.

18 d require little environmentally deleterious fertilizers.

19 in larger amounts, as from application of N fertilizers.

20 ddition from either atmospheric pollution or fertilizers.

21 el, and +0.4% (n.s.) for offset of inorganic fertilizers.

22 er than that of rock phosphate based mineral fertilizers.

23 olution as a function of at least one of the fertilizers.

24 rce for the future production of recycling P-fertilizers.

25 o, if not greater than, those of synthetic N fertilizers.

26 ucing the need for nonrenewable, polluting P fertilizers.

27 nsumption of nitrogen (N) and phosphorus (P) fertilizers.

28 rogen (N) and reduce the need for industrial fertilizers.

29 chniques used for coated, controlled-release fertilizers.

30 in agricultural areas and the application of fertilizers.

31 living N fixation in response to N, P and Mo fertilizers.

32 the organic (128.6 mg/100 g FW) and mineral fertilizer (125.5 mg/100 g FW) treatments.

33 in Nebraska that received large nitrogen (N) fertilizer (183 kg of N . ha(-1)) and irrigation water i

34 ith increasing application rates of silicate fertilizer; (2) Strong positive correlations between phy

35 contained CH 4 emissions observations from N fertilizer (28-406 kg N ha(-1) ) treatment and its contr

36 aerobic crops when yields are optimized by N fertilizer addition.

37 ecoming Cu-limited but are N-rich because of fertilizer addition.

38 based on short-term isotope-labelled mineral fertilizer additions should be questioned.

39 2.17 x 10(6) tonnes CO2 yr(-1) with silicate fertilizer additions.

40 4 x 10(6) tonnes CO2 yr(-1) without silicate fertilizer additions.

41 in a glasshouse, with organic and/or mineral fertilizers administered to meet nitrogen requirements.

42 Fertilizer administration provides a discriminant classi

43 ultivation, with the use of ammonium nitrate fertilizer alone accounting for around 40%.

44 FDFO product water rather than using single fertilizer alone.

45 d by rendering into feather meal and sold as fertilizer and animal feed, thereby providing a potentia

46 term mitigation strategies that manipulate N fertilizer and crop rotation to maximize crop N uptake w

47 Both the input of nitrogen fertilizer and cropland expansion benefited cereal aphid

48 ultural intensification (increasing nitrogen fertilizer and cropland expansion) can destabilize the i

49 as application of manure instead of chemical fertilizer and decreasing nitrogen input rate need to be

50 alfa-alfalfa) managed with lower synthetic N fertilizer and herbicide inputs and periodic application

51 e able to detect positive yield responses to fertilizer and hybrid seed inputs and that the inferred

52 bread production on the unsustainable use of fertilizer and illustrate the detail needed if the actor

53 of native forest soils, and likely decreased fertilizer and irrigation demands.

54 Using a 27-year-long inorganic fertilizer and manure amendment experiment in a maize (Z

55 crop P uptake as a function of P inputs from fertilizer and manure and to estimate P requirements for

56 Cumulative inputs of P fertilizer and manure for the period 1965-2007 in Europe

57 rop-specific, spatially explicit synthetic N fertilizer and manure N inputs to provide subnational ac

58 ersheds of the Mississippi River in St. Lawn fertilizer and pet waste dominated N and P inputs, respe

59 Two experiments compared the influence of fertilizer and shade on mycorrhizas in Andropogon gerard

60 compositions (delta(114/110)Cd) of archived fertilizer and soil samples from a 66 year-long agricult

61 ormonally active compounds in manure used as fertilizer and thereby affect the overall endocrine-disr

62 Emissions of N2O were induced by N fertilizer and vinasse applications.

63 advances in the use of "biologicals" as bio-fertilizers and biocontrol agents for sustainable agricu

64 it enters soils via Cd-containing phosphate fertilizers and endangers human health when taken up by

65 gnificantly faster than linear for synthetic fertilizers and for most crop types.

66 2-yr rotation (maize-soybean) that received fertilizers and herbicides at rates comparable to those

67 Given the high costs of fertilizers and in light of the fact that phosphate rock

68 productivity of agricultural crops, chemical fertilizers and other anthropogenic sources of fixed nit

69 Over-use of N fertilizer (and/or manure) and a declining groundwater t

70 cal fertilization, manure incorporation with fertilizer, and fertilizer with straw return treatments.

71 this N, atmospheric deposition, wastewater, fertilizer, and other agricultural sources are well-know

72 baceous plants when grown without applying N fertilizer; and bioenergy grasses, especially Miscanthus

73 ions from other NH3 and CH4 sources, such as fertilizer application and fossil fuel development, and

74 rgest sources of N2O emissions with nitrogen fertilizer application being the main driver of rising a

75 Results indicate that even if fertilizer application ceased, it may take years to see

76 Practices like fertilizer application have favoured biomass growth and

77 Fossil fuel combustion and fertilizer application in the United States have substan

78 However, nitrogen fertilizer application is expensive and negatively affec

79 Farms using single fertilizer application methods in general had a larger G

80 ecially Miscanthus, generally require less N fertilizer application than row crops and herbaceous pla

81 ed storm events, interacting with changes in fertilizer application timing and rate, as well as manag

82 uggests that relatively large increases in N fertilizer application would generate relatively small i

83 ion, land use, and land cover changes, and N fertilizer application) to simulate the concurrent impac

84 s, NANI was particularly sensitive to farm N fertilizer application, cattle N consumption, N fixation

85 Adsorbed As(III) could be removed prior to fertilizer application, however coprecipitated As(V) wil

86 When soil N was high due to fertilizer application, N2O emissions were higher during

87 solved oxygen, crops and irrigated cropland, fertilizer application, seasonally high water table, and

88 Fatty acids were influenced by breed and fertilizer application.

89 es were area of production and the method of fertilizer application.

90 n of new management practices (i.e. chemical fertilizer application/mechanization).

91 ency severely limits crop yield, and regular fertilizer applications are required to obtain high yiel

92 dditions with or without ammonium or nitrate fertilizer applications at three levels.

93 Globally widespread phosphate fertilizer applications have resulted in long-term incre

94 nutrient management strategies, reduction of fertilizer applications, employing vegetative buffers, a

95 3(-) leachate load from soybean fields (no N fertilizer applied).

96 World-wide, large quantities of nitrogenous fertilizer are applied to ensure maximum crop productivi

97 ssil fuel and geological reservoirs of other fertilizers are headed toward possible scarcity, increas

98 indicate that blending of two or more single fertilizers as draw solution (DS) can achieve significan

99 genetically modified crops, pesticides, and fertilizers; (b) loss of nectar resources from flowering

100 A bioorganic fertilizer (BIO), formulated by combining this isolate w

101 educe emissions and to facilitate its use as fertilizer, but a systematic analysis of these technolog

102 ed with 2xORG were similar to those with MIN fertilizer, but they contained more Ca and Mg.

103 in the fruit pulp was similar with all three fertilizers, but the calcium (Ca) and magnesium (Mg) was

104 Enhanced accumulation of (15)N-labeled fertilizer by transgenic lettuce compared with control p

105 taneously reduce the demand for both N and P fertilizers by up to 85%.

106 o those of soybeans treated with a regular P fertilizer (Ca(H2PO4)2).

107 A (15) N label in the fertilizer can be then used to trace the movement of the

108 ng apatite nanoparticles as a new class of P fertilizer can potentially enhance agronomical yield and

109 Repeated application of Cd-rich phosphate fertilizers can lead to the accumulation of this nonesse

110 riculture as highly effective phosphorus (P) fertilizers, cause surface water eutrophication, while s

111 However, due to extensive overuse of N fertilizer, China's cropland was found to show the least

112 swine manure, and freshwater with synthetic fertilizers) combined with emerging biomass conversion t

113 ated the 17 April 2013 explosion at the West Fertilizer Company (WFC) that resulted in 15 fatalities,

114 investigated the effects of three principal fertilizer components (nitrogen, phosphorus and potassiu

115 Only the use of fertilizer consistently results in reduced odds of food

116 Urine-derived fertilizers consistently contained 16S rRNA genes belong

117 lent to 8-25% of global inorganic phosphorus fertilizer consumption that year.

118 and the sludge produced by the WWTP, used as fertilizer, contains 2.6 x 10(5) ESBLEC per gram.

119 Consumer awareness, pesticide and fertilizer contaminations and environmental concerns hav

120 tegy to offset these issues by providing the fertilizer content in synchrony with the metabolic needs

121 p were evaluated when treated with a mineral fertilizer (control) (MIN) or cattle manure at a single

122 Controlled-release fertilizers (CRFs) can change the release kinetics of th

123 P sorption in soil by organic substances in fertilizers critically enhances the recyclability of P.

124 e Haber-Bosch process to produce ammonia for fertilizer currently relies on carbon-intensive steam re

125 As aggregated fertilizer data generate underestimation bias in nonline

126 HG inventories should improve assessments of fertilizer-derived N2O emissions, help address dispariti

127 s show that groundwater recharge containing (fertilizer-derived) nitrate drives the redox shift from

128 In fertilizer-drawn forward osmosis (FDFO) desalination, th

129 r flux to theoretical water flux) of blended fertilizer DS was observed to be between the PR of the t

130 a growing concern against its direct use as fertilizer due to contamination of the sludge with heavy

131 Therefore, providing silicate fertilizer during rice production may serve as an effect

132 Enhanced-efficiency fertilizers (EEFs) have been developed to better synchro

133 he first agronomic assessment of long-term N fertilizer effects on SOC with direct reference to N rat

134 waste aqueous extracts to be used as foliar fertilizer, enhancing the wine amino acid content especi

135 educing or eliminating the need for nitrogen fertilizer; enhancing the nutrient content of crop plant

136 he 'Green Revolution.' However, much of this fertilizer eventually ends up in rivers, lakes and ocean

137 cal Safety Board's investigation of the West Fertilizer Explosion.

138 trients (e.g., nitrogen and phosphorus) from fertilizers, fossil fuels, and human and livestock waste

139 However, blending fertilizers generally resulted in slightly reduced bulk

140 nuous maize cropping system with a 13 year N fertilizer gradient (0-269 kg N ha(-1) yr(-1)) that crea

141 Across the N fertilizer gradient, SOC in physico-chemically protected

142 Nutrients released into soils from uncoated fertilizer granules are lost continuously due to volatil

143 Between 8-12% of the applied fertilizer had leaked toward the hydrosphere during the

144 These data suggest that excessive N fertilizer had little effect on SOM and they complement

145 None of the fertilizers had a direct effect on the change of Wi (Del

146 Application of nitrogen fertilizer has altered terrestrial ecosystems.

147 But the use of urine as fertilizer has several constraints, such as, the high co

148 Plots that stopped receiving inorganic N fertilizer in 1989 recovered much of the diversity that

149 ; therefore it has been successfully used as fertilizer in different crops.

150 ed the fate of isotopically labeled nitrogen fertilizers in a three-decade-long in situ tracer experi

151 erm legacy of past applications of synthetic fertilizers in agricultural systems and the nitrogen ret

152 n attenuate arsenic contamination from green fertilizers in moderately acidic soils.

153 Nitrogen fertilizers increase crop growth as well as alter CH 4 p

154 Results have indicated that N fertilizers increased CH 4 emissions in 98 of 155 data p

155 Our study with 11 selected fertilizers indicate that blending of two or more single

156 the population dynamics of cereal aphids are fertilizer input and mean temperature in February, while

157 three models indicated processes of nitrogen fertilizer input at the land surface, transmission throu

158 as sustainable crop production with reduced fertilizer input or in resource-limited environments.

159 ion history and production potential under a fertilizer input scenario.

160 teristics (wheat proportion, crop diversity, fertilizer input, and wheat yield per unit area) and dam

161 oduction through more efficient use of their fertilizer input.

162 NO emissions followed a sigmoid response to fertilizer inputs and have emission factors under 1% for

163 ion is the nonlinearity between nitrogen (N) fertilizer inputs and on-site N emissions resulting from

164 oting endophytes has the potential to reduce fertilizer inputs through the enhancement of biological

165 m a corn-soybean rotation managed at three N fertilizer inputs with and without a winter cover crop i

166 Compared to low fertilizer inputs, high fertilizer treatments induced pl

167 Among the fertilizer inputs, nitrogen had the strongest effect on

168 ops with sustainable yields under reduced Pi fertilizer inputs.

169 rate natural abundance (13) C-CO2 and (15) N fertilizer into the metabolic plant components.

170 in the environment, the use of biosolids as fertilizer is a potential route for antidepressants to e

171 Industrially produced N-fertilizer is essential to the production of cereals tha

172 Inorganic N fertilizer is perhaps the most important factor affectin

173 lt of a growing population, the demand for P fertilizer is steadily increasing.

174 is supplied, while the pollution risk of the fertilizer is substantially lowered.

175 accumulation, arsenic-amended litter use as fertilizer is thought to be unsustainable.

176 many developing countries, increased use of fertilizers is a response to increase demand for rice.

177 ere biosolids have been used as agricultural fertilizers is an environmental concern.

178 he fact that phosphate rock, the source of P fertilizer, is a finite natural resource, there is a nee

179 te (MgNH4PO4.6H2O), a potential slow-release fertilizer, is highly attractive, but costly if large am

180 cks in 1998 AD, and a corresponding shift in fertilizer isotope composition.

181 nitrogen loss, developed using loss control fertilizer (LCF) prepared by adding modified natural nan

182 rine can be processed into market-attractive fertilizers like struvite; however, concerns regarding t

183 Organic fertilizers, like cattle manure, have emerged as an impo

184 function of different nitrogen and potassium fertilizer loads.

185 sses across the crop rotation, and (ii) if N fertilizer management and the inclusion of a winter cove

186 e precise but more challenging paradigm in P fertilizer management that seeks to develop more sustain

187 cultivars, adoption of appropriate water and fertilizer management, bioremediation, and change of lan

188 icultural pesticides, solvents, and chemical fertilizers may increase the risk of RA in women, while

189 athogenic fungi, ammonium nitrate (e.g. from fertilizers) may enhance biocontrol potential in some ci

190 to manure (Org-M) in comparison to chemical fertilizers (Min-F) or non-fertilizers (Non-F).

191 prudent use requires firstly eliminating any fertilizer mismanagement plus the implementation of know

192 Urea is the nitrogen fertilizer most utilized in crop production worldwide.

193 the EF was not significantly different from fertilizer N alone.

194 , those systems with cover crops and reduced fertilizer N emitted more N2 O during the corn and soybe

195 have been demonstrated, the transit times of fertilizer N in the pedosphere-hydrosphere system are po

196 s) have been developed to better synchronize fertilizer N release with crop uptake, offering the pote

197 to which extent and over which time periods fertilizer N stored in soil organic matter is rereleased

198 u tracer experiment that quantified not only fertilizer N uptake by plants and retention in soils, bu

199 up by plants, whereas 12-15% of the labeled fertilizer N were still residing in the soil organic mat

200 ity as addition of 54 kg . ha(-1) . y(-1) of fertilizer N, and was as influential as removing a domin

201 O emissions compared to the use of synthetic fertilizer N.

202 We found that 61-65% of the applied fertilizers N were taken up by plants, whereas 12-15% of

203 1 Tg of N, of which 48% was supplied through fertilizer-N and 4% came from net soil depletion.

204 refore, in humid climates, deep placement of fertilizer-N is recommended when implementing NT/RT.

205 When fertilizer-N was placed at >/=5 cm depth, NT/RT signific

206 scaled N2 O emissions in humid climates when fertilizer-N was placed at >/=5 cm depth.

207 s to test the hypothesis that in response to fertilizer nitrogen (N) addition, yield-scaled global wa

208 k response from sugar cane soil treated with fertilizer nitrogen (N) and vinasse applied separately o

209 used readily available data comprising farm fertilizer nitrogen (N), weather data, and soil properti

210 rison to chemical fertilizers (Min-F) or non-fertilizers (Non-F).

211 udes that manure incorporation with chemical fertilizer not only can achieve high N use efficiency an

212 chemical nitrogen, phosphorus and potassium fertilizers (NPK), and combined manure and chemical fert

213 zers (NPK), and combined manure and chemical fertilizers (NPKM1, NPKM2).

214 CRFs) can change the release kinetics of the fertilizer nutrients through an abatement strategy to of

215 em can be developed to remove selenium (Se), fertilizer nutrients, and other contaminants.

216 This study evaluated the influence of NPK fertilizer on protein, fibre, ash, fat, carbohydrate, an

217 cross N rates, suggesting little effect of N fertilizer on soil organic matter (SOM) after decomposit

218 gnificance due to sustained use of inorganic fertilizers on agricultural soils.

219 controlling factors to predict effects of N fertilizers on CH 4 emissions in rice soils.

220 bial processes that control net effects of N fertilizers on CH 4 emissions in rice soils.

221 rsial reports on net impacts of nitrogen (N) fertilizers on methane (CH 4 ) emissions.

222 wastewater with no external input of water, fertilizer or CO(2).

223 ion or denitrification and minimal impact of fertilizer or deposition N sources.

224 nitrogen as ammonium from urine for use as a fertilizer or disinfectant.

225 associated with the application of chemical fertilizers (OR = 1.7; 95% CI: 1.1, 2.7) and cleaning wi

226 tively, is contributed by sources other than fertilizer- or soil-N.

227 ure at a single dose equivalent to potassium fertilizer (ORG) or double dose (2xORG).

228 ffects can be obtained by applying mineral N fertilizers over the soil or forest canopy.

229 their temporal structure in maize-roots with fertilizer P application over a three-year period.

230 , and new innovative technologies to improve fertilizer P recovery.

231 oluble phosphate rock (PR-soil) or soluble P fertilizer (P-soil).

232 ing four major types of EEFs (polymer-coated fertilizers PCF, nitrification inhibitors NI, urease inh

233 (low mechanical input and infrequent use of fertilizers, pesticides and herbicides), and also domina

234 ith fixed infrastructures and high inputs of fertilizers, pesticides, and irrigation.

235 for the heating of greenhouses, irrigation, fertilizers, pesticides, storage and transport to and wi

236 tural states, the surplus of added inorganic fertilizer phosphorus retained by soils post harvest is

237 e demonstration areas compared with farmers' fertilizer practices (FFP), respectively.

238 While avoided fertilizer production does reduce potential impacts, pho

239 hen transported by truck to regeneration and fertilizer production facilities.

240 ble use of SSA as secondary raw material for fertilizer production it should be noted that its Cd and

241 agement via nitrification-denitrification if fertilizer production offsets are taken into account.

242 g., cropping, livestock raising, irrigation, fertilizer production, tractor use) in the Great Plains

243 se offset by operational savings and avoided fertilizer production.

244 ric deposition (range 43-71%) and chemical N fertilizers (range <1-49%) were the dominant NO3-N sourc

245 Nitrogen (N) fertilizer rate is the best single predictor of N2O emis

246 ically protected pools was not affected by N fertilizer rate or residue inputs.

247 Between the control and the highest fertilizer rate, proximate compositions decreased by 7-6

248 -1) Yield is possible by reducing N chemical fertilizer rates, along with intermittent flooding in pa

249 common biomineral and increasingly important fertilizer recovered from wastewater treatment plants, i

250 ruvite that is an increasingly popular green fertilizer recovered from wastewaters.

251 AD first for fertilizer replacement, with AC second, and AC and AD ti

252 ntify one such material cost, the phosphorus fertilizer required to intensify global crop production

253 e regulation of a single gene, for phosphate fertilizer responsiveness/arsenate tolerance in wild gra

254 d more resources than were offset by avoided fertilizers, resulting in a net environmental burden.

255 mic acids (HA), and the synthetic oleophilic fertilizer S-200 were used as representatives of fresh,

256 tive management of lucerne fields, phosphate fertilizer should be applied and cutting performed.

257 in fruits to be maintained, little or no NPK fertilizer should be applied.

258 Applied nitrogen (N) fertilizer significantly increases the leaf yield.

259 was observed to be between the PR of the two fertilizer solutions tested individually.

260 Effects of N fertilizer stimulated Methanotrophs in reducing CH 4 emi

261 esistomes, and that the addition of nitrogen fertilizer strongly influenced soil ARG content.

262 Lastly, we assert that fertilizer subsidies may not be sufficient or sustainabl

263 transgenic rice under different levels of N-fertilizer supply, we investigated the biomass, exogenou

264 e, especially with appropriate increase of N fertilizer supply, while, to some extent, the exogenous

265 e amounts of P are mined annually to produce fertilizer that is applied in support of the 'Green Revo

266 ted with the production of external nitrogen fertilizers, the manner in which nitrogen is supplied to

267 lting from localized spreading of boron-rich fertilizers, thus indicating a significant local impact

268 astewater treatment biosolids are applied as fertilizer to agricultural soils.

269 s, the application of synthetic nitrogen (N) fertilizer to farmland resulted in a dramatic increase i

270 anure is applied to rangelands as an organic fertilizer to stimulate forage production, but the long-

271 correlations between application rates of N fertilizers to agricultural soils and nitrate contaminat

272 determination of ammonium in wastewaters and fertilizers to demonstrate the applicability of the syst

273 * Whilst shoot ionomes were sensitive to fertilizer treatment, phylogenetic variation in a subset

274 th plant species, and responded similarly to fertilizer treatments in diverse plant species.

275 archived herbage samples from 16 contrasting fertilizer treatments in the Park Grass Experiment, Roth

276 Compared to low fertilizer inputs, high fertilizer treatments induced plant growth but also favo

277 Subplots had received contrasting fertilizer treatments since 1856.

278 texture, tillage duration, crop species, and fertilizer type were used as co-varying factors.

279 a comparable evolution as a function of both fertilizer types.

280 Nitrogen fertilizer unabsorbed by crops eventually discharges int

281 hat takes into account high-yield cultivars, fertilizer use and irrigation, we find that the long-ter

282 Order-of-magnitude increases in fertilizer use are seen as a critical step in attaining

283 Improved nutrient acquisition can increase fertilizer use efficiency and is critical for crop produ

284 tural resource, there is a need to enhance P fertilizer use efficiency in agricultural systems and to

285 heric ozone pollution and improving nitrogen fertilizer use efficiency.

286 We estimate that average global P fertilizer use must change from the current 17.8 to 16.8

287 ogen flux to the coast, related to increased fertilizer use required to feed an expanding human popul

288 wering watershed N export (e.g., by reducing fertilizer use).

289 e toxicity, and nontoxic emissions linked to fertilizer use.

290 d with about one-quarter of land, water, and fertilizer used for crop production, even though resourc

291 astewater with the same mass of nutrients as fertilizers used to produce crops containing 10-75 days'

292 The chemical N fertilizer uses were estimated to increase GWP by 45.6 +

293 carbon >1.5% and soils with pH <7, and where fertilizer was applied only once annually.

294 Although N fertilizer was negatively linearly correlated with POM C

295 Response of CH 4 emissions per kg N fertilizer was significantly (P < 0.05) greater at < 140

296 Overall, response of CH 4 emissions to N fertilizers was correlated with N-induced crop yield (r

297 g on plots with the addition of both N and P fertilizer were significantly higher than that of plants

298 ter input-use efficiencies, especially for N fertilizer, were responsible for better performance of t

299 n, manure incorporation with fertilizer, and fertilizer with straw return treatments.

300 nd phosphorus are among the most widely used fertilizers worldwide.