ライフサイエンスコーパス: earthworm

1 50% of the energy was allocated to annelids (earthworms).

2 ults showed that MCs could bioaccumulated in earthworm.

3 at was absent from soil yet observed in most earthworms.

4 nt protective effects against Cu toxicity to earthworms.

5 rmed As accumulation in the coelom of intact earthworms.

6 spatio-temporal database of introduced alien earthworms.

7 nd adapted for feeding on social insects and earthworms.

8 e rotifers, freshwater mussels, daphnids and earthworms.

9 low and deep soil, perhaps through mixing by earthworms.

10 hich suggests size-selective egestion by the earthworms.

11 increased soil C storage in the presence of earthworms.

12 The (68)Znen/(64)Znen ratios determined for earthworms (1.09 +/- 0.04), soils (1.09 +/- 0.02), and p

13 redators, suspension feeders and terrestrial earthworms(1).

14 ty increased in inoculated seedlings without earthworms 12 months after inoculation, and general nega

15 Further, a field study on earthworms (18 pooled samples) in sludge-amended soil wa

16 tip density in inoculated seedlings without earthworms 6 months after inoculation, lower fine root t

17 on agriculture [CA]) significantly increased earthworm abundance (mean increase of 137% and 127%, res

18 production of key crops by analyzing maps of earthworm abundance, soil properties, and crop yields to

19 phytoaccumulation was minimal (BAF(dw) < 1), earthworms accumulated high loads (BAF(dw) up to 23), su

20 es Darwin, but several recent syntheses link earthworm activities to higher greenhouse gas emissions,

21 ot system parameters and mycorrhization, how earthworms affect the bare root system, and if mycorrhiz

22 ray and finally study slices within a living earthworm, allowing metabolite changes to be discerned w

23 ht; (c) set-up of the control plots (i.e. no earthworms, ambient nitrogen) used in this experiment.

24 derstand the joint effects of TNT and RDX on earthworms, an important ecological and bioindicator spe

25 We collected 52 earthworm and soil samples from arable and forest ecosys

26 oil RQ values indicated low level of risk to earthworms and arthropods.

27 0 +/- 2670 and 3000 +/- 200 mug/kg lipid for earthworms and detritivorous woodlice, respectively).

28 Snails, earthworms and flatworms are remarkably different animal

29 n nature, from individual organisms (notably earthworms and hydra), through communities of microbes,

30 ion site and is nontoxic to nerve tissues in earthworms and mammals, we have also developed in vivo p

31 oken down through the synergistic actions of earthworms and microbial communities.

32 However, in plots receiving both exotic earthworms and N addition, such earthworm effects on the

33 three-level food web of predaceous beetles, earthworms and plants, Zhao et al. (2013) report evidenc

34 ommon in plants and bees but intermittent in earthworms and spiders.

35 We conclude that the coordinated actions of earthworms and their associated soil biota were responsi

36 of these two important ecological groups of earthworms and their burrowing, feeding and casting acti

37 High abundance of an invasive pantropical earthworm (and the absence of indigenous lumbricid speci

38 the endogeic Aporrectodea rosea (rosy-tipped earthworm) and planted with Lolium perenne (perennial ry

39 tional groups of termites, ants, beetles and earthworms, and an increase in the abundance of small ma

40 This suggests that earthworms, and probably other soil organisms, constitut

41 to homologous genes from crayfish, insects, earthworms, and sea urchins.

42 and 'brown' belowground (soil arthropods and earthworms) animal food webs in tropical rainforests and

43 ting key ecological functions: trees, fungi, earthworms, ants and spiders.

44 and if mycorrhization parameters change when earthworms are added to the inoculation substrate.

45 Earthworms are among the most important soil dwelling in

46 our study provides evidence that introduced earthworms are associated with declines in plant diversi

47 Earthworms are critical in regulating soil processes and

48 Earthworms are critical soil ecosystem engineers that su

49 Earthworms are globally distributed and perform essentia

50 As a consequence, soil taxa such as earthworms are iconic in good land management practices.

51 Our findings suggest that earthworms are important drivers of global food producti

52 Our results therefore imply that earthworms are of crucial importance to decrease the yie

53 Soil organisms, including earthworms, are a key component of terrestrial ecosystem

54 However, earthworms as major detritivores stayed unchanged in the

55 The earthworm-associated microbiome differs from the surroun

56 Earthworm Au concentrations were continuously monitored

57 The positive effects of earthworms become larger when more residue is returned t

58 ake and elimination pathways when predicting earthworm bioconcentration.

59 that correlated with soil C content, such as earthworm biomass and fungal/bacterial energy channel ra

60 groups) tended to decrease, with increasing earthworm biomass.

61 a case study on the role of root growth and earthworm bioturbation in restoring the structure of a s

62 ated AC were comparable to those measured by earthworm biouptake (bioavailability) at both dose level

63 doalkyl betaine (6:2 FTAB) bioaccumulated in earthworms [BSAF ~ 2.5-5.4 (g(dw,worm)/g(dw,soil))(-1)]

64 ficant effects on the survival and growth of earthworms, but significantly reduced cocoon and juvenil

65 act as vectors to increase metal exposure in earthworms, but that the associated risk is unlikely to

66 n dating protocol has been developed to date earthworm calcite granules from the reference loess sequ

67 Soft organisms such as earthworms can access confined, narrow spaces, inspiring

68 Bacterial and fungal communities of earthworm casts were mainly composed of microbial taxa n

69 ecific cellular or molecular level damage to earthworms caused by chronic exposure to TiO(2) are warr

70 a distinct bacterial community defines these earthworms, clear family- and species-level modification

71 cal improvements enabled by the radiocarbon "earthworm clock" thus strongly enhance our understanding

72 in cytotoxicity of dissolved silver salt on earthworm coelomocytes and human cells (THP-1 cells, dif

73 ate change may have serious implications for earthworm communities and for the functions they provide

74 ect sizes of associations between introduced earthworm communities and plant diversity, cover of plan

75 We compiled a global dataset of sampled earthworm communities from 6928 sites in 57 countries as

76 s were found to be more important in shaping earthworm communities than soil properties or habitat co

77 We identified a core earthworm community comprising Proteobacteria ( approxim

78 this reflects the phylogenetic uniqueness of earthworms compared to the well-annotated model animals.

79 evaluated against a data set of 402 internal earthworm concentrations reported from the literature in

80 Nanoplastics were detected in depurated earthworms confirming their uptake without any detectabl

81 specially notable in the global South, where earthworms contribute 10% of total grain production in S

82 Our findings indicate that earthworms contribute to roughly 6.5% of global grain (m

83 The earthworm contribution is especially notable in the glob

84 ses or control cauterization with artificial earthworms covered with earthworm wash (EWW) or distille

85 revealed that detrimental warming effects on earthworm densities and biomass could indeed be partly e

86 effects depends on presence of crop residue, earthworm density and type and rate of fertilization.

87 ults indicate that PFAA bioaccumulation into earthworms depends on soil concentrations, soil characte

88 oluminescent systems (those of limpet Latia, earthworms Diplocardia and Fridericia and higher fungi),

89 ntries as a basis for predicting patterns in earthworm diversity, abundance, and biomass.

90 nin, a pore-forming toxin extracted from the earthworm E. fetida, inserts large conductance nanopores

91 by polyoxymethylene (POM) passive uptake and earthworm (E. fetida) biouptake.

92 lined with increasing richness of introduced earthworm ecological groups.

93 Focused on the soil-earthworm ecosystem, we for the first time deciphered th

94 cal disturbances should encourage beneficial earthworm effects and support multiple ecosystem service

95 both exotic earthworms and N addition, such earthworm effects on the nematode community were negated

96 ed weekly throughout the life history of the earthworm Eisenia andrei to test the hypothesis that the

97 nin, a sphingomyelin-specific toxin from the earthworm Eisenia fetida [10, 11].

98 Lysenin from the coelomic fluid of the earthworm Eisenia fetida belongs to the aerolysin family

99 ular and cellular toxicity mechanisms in the earthworm Eisenia fetida exposed to AgNPs (83 +/- 22 nm)

100 The earthworm Eisenia fetida is one of the most used species

101 oparticle recognition by coelomocytes of the earthworm Eisenia fetida using E. fetida coelomic protei

102 that such dual strokes occur as well in the earthworm Eisenia fetida which inhabits moist sediments

103 initro-1,3,5-triazacyclohexane (RDX), in the earthworm Eisenia fetida.

104 We thus exposed earthworms ( Eisenia fetida ) to artificial soil amended

105 investigate arsenic (As) bioaccumulation in earthworms (Eisenia andrei) exposed to six field-collect

106 , 1, 3, 6, and 12 months of soil incubation, earthworms (Eisenia andrei) were introduced for 72 h exp

107 re compared to actual PAH bioaccumulation in earthworms (Eisenia fetida) and rye grass (Lolium multif

108 ccumulation factors (BSAFs) were assessed in earthworms (Eisenia fetida) exposed to soil microcosms a

109 Uptake of PFAAs by earthworms (Eisenia fetida) exposed to unspiked soils wi

110 Earthworms (Eisenia fetida) were exposed to Au NPs in ar

111 erns, and biomagnification of PFASs in soil, earthworms (Eisenia fetida), and Bank voles (Myodes glar

112 copolymers were assessed in laboratory-grown earthworms (Eisenia fetida, triplicate of exposure tests

113 Lysenin is a pore-forming toxin from the earthworm Eisenida foetida, of which both the soluble an

114 Specifically, earthworms enhanced multifunctionality by shifting the f

115 od for maintaining the prostate gland of the earthworm, Eudrilus eugeniae ex vivo and examine its pot

116 for estimating pesticide bioconcentration in earthworms exhibit limited applicability across differen

117 extracts of E. fetida tissue suggested that earthworms exhibited significant changes in their metabo

118 Individual Lumbricus terrestris earthworms exposed for 28 days in mesocosms of 260 g moi

119 In earthworms exposed to Ansulite and Arctic Foam aqueous f

120 Earthworms exposed to lyocell had a marginal growth redu

121 ully identified CMTT particles in laboratory earthworms exposed to soil spiked with CMTT.

122 Two metabolites were detected in the earthworms exposed to the C4-FASA-based copolymer: perfl

123 tperformed existing models in characterizing earthworm exposure to pesticides in soil, but it could a

124 dings support the hypothesis that introduced earthworms facilitate particular plant species adapted t

125 oxicological effect of microcystins (MCs) on earthworms, filter paper acute toxicity test, avoidance

126 The reduction efficiencies measured by earthworm for coconut AC and corn stover biochar were ge

127 vel luciferin from a bioluminescent Siberian earthworm Fridericia heliota was recently described.

128 CHEMHIST upon in situ imaging, we sampled an earthworm from its natural habitat and created an intera

129 This shows that drilodefensins protect earthworms from the harmful effects of ingested polyphen

130 20-induced neurotoxicity and the recovery of earthworms from transient neurotoxicity stress.

131 he probably continuous introduction of alien earthworms, from a variety of sources and introduction p

132 s at the cut ends of invertebrate myelinated earthworm giant axons beginning with the formation of a

133 structures, which form after transection of earthworm giant axons, are very dynamic in the short ter

134 ene, earthworm wash vapor, fish water vapor, earthworms, goldfish) but not water vapor.

135 insights into the variations of ARGs in the earthworm gut and highlight the vital role of viruses in

136 the geographic patterns and main drivers of earthworm gut ARGs remain largely unknown.

137 ve disruption of microbiome and resistome in earthworm gut by chiral fungicides and offer significant

138 act the inhibitory effects of polyphenols on earthworm gut enzymes, and high-polyphenol diets increas

139 The earthworm gut had a lower frequency of co-occurrence pat

140 il solution (0.01 M CaCl2), but in synthetic earthworm guts desorption was higher from microplastics

141 Earthworm guts harbored a lower diversity and abundance

142 Earthworms have been perceived as benevolent soil engine

143 ibility of maintaining the prostate gland of earthworms in an ex vivo setting, providing a valuable m

144 sment underlined a moderate to high risk for earthworms in arable soils mostly attributed to insectic

145 t at two sites in Minnesota, USA by sampling earthworms in closed and open canopy in three temperatur

146 e FASA-based copolymers were taken up by the earthworms in concentrations between 19 and 33 ng/g of d

147 suggest that warming limits the invasion of earthworms in northern North America by causing less fav

148 and offspring generations of two species of earthworms in order to evaluate possible mechanisms of a

149 ercial mycorrhization with truffles, and how earthworms in the inoculation substrate would affect the

150 Earthworms inhabiting highly contaminated soils bare clo

151 It is unclear how earthworms interact with soil management practices, maki

152 et al. () explored how N addition and exotic earthworms interacted to impact on the plant-feeding nem

153 (particularly the plasmid-borne ARGs) in the earthworm intestinal microbiome.

154 species adapted to the abiotic conditions of earthworm-invaded forests.

155 t region that to date supposedly have slowed earthworm invasion, future warming is hypothesized to ac

156 ies richness or evenness did not change with earthworm invasion, our results indicate clear changes i

157 future warming is hypothesized to accelerate earthworm invasions into yet non-invaded regions.

158 e and soil macro-organism (RQs > 1), but for earthworms it was safe (RQs < 1).

159 een the uptake of the two forms of Zn by the earthworm L. rubellus, with the dietary pathway accounti

160 Earthworm-like crawlers realize locomotion through in-pl

161 this obstacle can be removed by our proposed earthworm-like peristaltic crawling motion mechanism, ba

162 robotic control problems by a case study of earthworm-like peristaltic crawling without traditional

163 d.w.), and higher concentrations of PFAS in earthworms living in sludge-amended soil compared to non

164 , uptake pathways by, and biokinetics in the earthworm Lumbricus rubellus were investigated using sta

165 , we studied the survival and fitness of the earthworm Lumbricus terrestris (Oligochaeta, Lumbricidae

166 The extracellular hemoglobin of the earthworm Lumbricus terrestris has four major kinds of O

167 hexagonal bilayer hemoglobin (HBL Hb) of the earthworm Lumbricus terrestris provided masses of 3.41 t

168 Many annelids, including the earthworm Lumbricus terrestris, have giant cooperative r

169 er hemoglobin (Hb) and its subunits from the earthworm Lumbricus terrestris.

170 astics in microcosms with the deep-burrowing earthworm Lumbricus terrestris.

171 ability models for predicting Cu toxicity to earthworms (Lumbricus rubellus, Aporrectodea longa, and

172 trate here the formation of PFOA and PFOS in earthworms (Lumbricus terrestris) from a group of four z

173 b encompassing land-applied biosolids, soil, earthworms (Lumbricus), deer mice (Peromyscus maniculatu

174 Populations of the earthworm, Lumbricus rubellus, are commonly found across

175 The extracellular hemoglobin (Hb) of the earthworm, Lumbricus terrestris, has four major O2-bindi

176 tion of exposure, and that accumulation into earthworms may be a potential route of entry of PFAAs in

177 ts indicated that the conduction velocity of earthworm medial giant nerve fiber decreased significant

178 However, earthworm-mediated changes in soil physical structure, p

179 The observed earthworm metabolic changes appeared to be consistent wi

180 Finally, an earthworm metallothionein-GFP construct could be activat

181 higher on the experimental site in the soil, earthworms, mice (livers), and European starling eggs, b

182 s implications to its functional role in the earthworm microbiome.

183 o be integrated with models that account for earthworm movement and fluctuating soil pesticide concen

184 in vivo procedures that permanently maintain earthworm myelinated medial giant axons whose functional

185 cterizing the major metal-binding protein in earthworms, namely the two isoforms of metallothionein.

186 een the 2 arms of a maze containing airborne earthworm odor as compared with a blank control.

187 Preoperatively, exposure to earthworm odor produced more frequent and shorter durati

188 snakes exhibited differential responding to earthworm odors.

189 inoculation, and general negative effect of earthworm on branching density.

190 the multiple direct and indirect impacts of earthworms on ecosystem functions within an ecological m

191 We estimate the impacts of earthworms on global production of key crops by analyzin

192 The effect of earthworms on mycorrhization of silver fir with Tuber ae

193 for the first time the impacts of introduced earthworms on plant diversity and community composition

194 earch has ignited debate about the effect of earthworms on the GHG balance of soil.

195 aquatic (snail and mussel) and terrestrial (earthworm) organisms and for monitoring the environmenta

196 n soil water content (SWC) can also decrease earthworm performance.

197 at inactivated coelomic fluid (HI-CF) of the earthworm, Perionyx excavatus as a potential alternative

198 burrowing horizontally to acquire nutrients) earthworm Pontoscolex corethrurus that was added to the

199 cide glyphosate did not significantly affect earthworm population responses to RT.

200 Earthworm population responses were more pronounced when

201 ecological policies and practices to support earthworm populations and overall soil biodiversity coul

202 ultivation practices is expected to increase earthworm populations and their contributions to ecosyst

203 orted on the effects of tillage intensity on earthworm populations, attributed in narrative reviews t

204 Here, we show that earthworms possess a class of unique surface-active meta

205 s that favor growth-promoting rhizobacteria, earthworms, predatory mites, and other beneficial organi

206 They demonstrate that exotic earthworm presence alone increased the abundance of less

207 escribing 21 ecosystem functions showed that earthworm presence generally enhanced multifunctionality

208 e show, using meta-analysis, that on average earthworm presence in agroecosystems leads to a 25% incr

209 show, in a unique two-year experiment, that earthworm presence increases the combined cumulative emi

210 Yet, studies on the effect of earthworm presence on crop yields have not been quantita

211 elevated CO2 , nutrient enrichment, drought, earthworm presence, or warming) were manipulated.

212 Because NT agriculture stimulates earthworm presence, our results identify a possible biol

213 Here we use earthworm primary cells, cross-referencing to human cell

214 We successfully maintained the earthworm prostate gland in cell culture media for over

215 weights were correlated to % weight loss in earthworm (r = -0.568, P = 0.028).

216 ed to examine the response of Eisenia fetida earthworms raised from juveniles for 20-23 weeks in soil

217 Earthworms reside in the most contaminated sites on eart

218 olomics provides a more sensitive measure of earthworm response to TiO(2) materials in soil and that

219 Mycorrhization with or without earthworms revealed contrasting effects on fine root bio

220 to determine total As within both the whole earthworm's body (AsE) and coelomic fluid extracts (AsF)

221 Here, we show that the earthworm's metal detoxification pathway can be exploite

222 two phyla (a waterbird, freshwater fish, and earthworms) sampled in different geographical areas and

223 The protein ES20, derived from earthworm shock secretion, is a vomeronasally mediated c

224 The accumulation of labeled Zn by the earthworms showed a direct relationship with the proport

225 city was found in the filter paper test, and earthworms showed no avoidance response to MCs exposure.

226 Digestion of the earthworms showed that they did not retain microplastics

227 m uptake and elimination studies using three earthworm species (Lumbricus terrestris, Aporrectodea ca

228 The invasion of European earthworm species across northern North America has seve

229 sts) on the springtail Folsomia candida, the earthworm species Aporectodea caliginosa and Eisenia fet

230 of Zn and Pb in thin sections of two epigeic earthworm species collected from a Pb/Zn-mine soil.

231 ilot-scale vermireactor for 91 days with the earthworm species Eisenia andrei.

232 We show that 70 alien earthworm species have colonized the North American cont

233 lating the developed toxicity models for one earthworm species to another species.

234 the neonicotinoid imidacloprid between five earthworm species, a critical nontarget taxon.

235 farm and regional levels by sampling plants, earthworms, spiders and bees in 1470 fields of 205 rando

236 This suggests that earthworms stimulate plant growth predominantly through

237 tic relationships, with the exception of the earthworm, suggesting that the reported presence of J ch

238 ts the Open Air Laboratories (OPAL) Soil and Earthworm Survey as an example of public participation i

239 In addition to the known earthworm symbiont (Verminephrobacter sp.), we identifie

240 diclofenac, fluoxetine, and orlistat in soil-earthworm systems.

241 ed in Shao et al. (): (a) the endogeic (i.e. earthworms that typically live in the soil, burrowing ho

242 It is unknown how earthworms, the major component of animal biomass in man

243 Earthworms thus repeatedly ingested and excreted nanopla

244 Detection and quantification of (68)Zn-E in earthworm tissue was possible after only 4 h of dermal e

245 Analyses of soils, pore waters, and earthworm tissues using multiple collector inductively c

246 The relative sensitivity of the earthworms to Cu in different soils followed the same or

247 the arsenious soils, the As distribution in earthworms was examined by micro-X-ray fluorescence spec

248 tion with artificial earthworms covered with earthworm wash (EWW) or distilled water.

249 f airborne odorants (amyl acetate, limonene, earthworm wash vapor, fish water vapor, earthworms, gold

250 mites), and soil biota (including mites and earthworms), we assess the impacts of synergistic intera

251 BDE-209 burdens in sludge-amended soil and earthworms were 7500 +/- 2800 mug/kg TOC and 6500 +/- 41

252 noculation, lower fine root tip density when earthworms were added, the specific root tip density inc

253 Earthworms were also collected in situ from a fire-equip

254 ta soil accumulation factors (BSAFs) for the earthworms were calculated after 28 days of exposure for

255 Residual zwitterionic/cationic PFAS in earthworms were detected at the end of the elimination p

256 Eighteen earthworms were exposed for 6 days to 0.2 mug/cm(2) of C

257 Standard wild-type Lumbricus rubellus earthworms were exposed to soil spiked with CdCl(2) and

258 The highest concentrations in the earthworms were for perfluorooctane sulfonate (PFOS) in

259 Nine vehicle control earthworms were sacrificed at days 6 and 13, separately.

260 d, more importantly, the bigger-sized anecic earthworms were the most sensitive ecological groups to

261 e compositions of the soils, pore waters and earthworms were then determined using multiple collector

262 suggest that MCs induces oxidative stress on earthworms, which leads to disruption of the antioxidant

263 (BMF) > 1 was detected for Bank vole(whole)/earthworm(whole) for perfluorooctansulfonate in the skii

264 ues of ecologically significant taxa such as earthworms will improve risk assessments.

265 Uptake routes were isolated by introducing earthworms with sealed and unsealed mouthparts into test

266 rs generally predicted PAH concentrations in earthworms within a factor of 10, although correlations

267 il properties, and crop yields together with earthworm-yield responses from the literature.