ライフサイエンスコーパス: earthworm

1 ults showed that MCs could bioaccumulated in earthworm.

2 hich suggests size-selective egestion by the earthworms.

3 increased soil C storage in the presence of earthworms.

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

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

6 nt protective effects against Cu toxicity to earthworms.

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

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

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

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

11 0 +/- 2670 and 3000 +/- 200 mug/kg lipid for earthworms and detritivorous woodlice, respectively).

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

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

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

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

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

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

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

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

20 Earthworms are among the most important soil dwelling in

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

22 Earthworms are globally distributed and perform essentia

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

24 The earthworm-associated microbiome differs from the surroun

25 Earthworm Au concentrations were continuously monitored

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

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

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

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

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

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

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

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

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

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

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

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

38 We identified a core earthworm community comprising Proteobacteria ( approxim

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

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

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

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

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

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

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

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

47 lined with increasing richness of introduced earthworm ecological groups.

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

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

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

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

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

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

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

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

56 , 1, 3, 6, and 12 months of soil incubation, earthworms (Eisenia andrei) were introduced for 72 h exp

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

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

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

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

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

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

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

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

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

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

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

68 20-induced neurotoxicity and the recovery of earthworms from transient neurotoxicity stress.

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

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

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

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

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

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

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

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

77 Earthworms inhabiting highly contaminated soils bare clo

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

97 The observed earthworm metabolic changes appeared to be consistent wi

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

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

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

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

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

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

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

105 snakes exhibited differential responding to earthworm odors.

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

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

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

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

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

111 Earthworm population responses were more pronounced when

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

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

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

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

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

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

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

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

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

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

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

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

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

125 Earthworms reside in the most contaminated sites on eart

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

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

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

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

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

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

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

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

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

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

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

137 This suggests that earthworms stimulate plant growth predominantly through

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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