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1 . acute and chronic tests (in the absence of Daphnia).
2  reproduction in the aquatic microcrustacean Daphnia.
3 tion in the aquatic key species of the genus Daphnia.
4 tness and epigenome of the keystone species, Daphnia.
5  movement of the appendages of the Crustacea Daphnia.
6 d Drosophila cells to model HIF signaling in Daphnia.
7  planktonic organisms such as the water flea Daphnia.
8 50 impairs nutrient utilization or uptake in Daphnia.
9 ession of nine genes potentially involved in Daphnia acclimation to cyanobacteria: six protease genes
10 50 (i.e., BZ54) were significantly higher in Daphnia after 48 h following 1/10 LC50 exposure.
11          Comparison with the model arthropod Daphnia allows some insights into defining characteristi
12 the functional responses of the small-bodied Daphnia ambigua and the larger Daphnia pulicaria.
13  these predictions in natural populations of Daphnia ambigua from lakes that vary in the severity and
14           Using new data for the zooplankter Daphnia ambigua, we also find genotypic variation in the
15  system genes from the cladoceran crustacean Daphnia and examined DNA sequence diversity.
16 unction was essential to the SSRI effects on Daphnia and linking them to the pharmacological effects
17                                          For Daphnia and other species, critical movement parameters
18 tems in defended and undefended genotypes in Daphnia and possibly in other prey organisms as well.
19  phytoplankton (chlorophyll a), zooplankton (Daphnia) and fish (perch, Perca fluviatilis) in two basi
20                     Zooplankton (Holopedium, Daphnia, and Leptodiaptomus) are comprised of approximat
21 gh an aquatic food chain, from algae through Daphnia, and studied the effects on behavior and metabol
22                                              Daphnia are found in lakes with (i) anadromous alewife (
23                                              Daphnia are rare year-round in 'landlocked lakes' and ar
24 , where cascades are usually seen when large Daphnia are the primary herbivores, but not when smaller
25    Our results confirm the attractiveness of Daphnia as a model organism, because the high nucleotide
26                                              Daphnia avoided the predators using the horizontal and v
27  these and other areas, as genomic tools for Daphnia become widely available to investigators.
28 in newly identified serotonin-neurons in the Daphnia brain mediate these effects.
29 pid accumulation in droplets is regulated in Daphnia by the interaction between the nuclear receptor
30                   Additionally, crustaceans (Daphnia, Caligus, and Lepeophtheirus) and some insects (
31 ts suggest a complex mechanistic response in Daphnia characterized by interactions between DNA methyl
32  citrate-nAg; (ii) Daphnia + predator; (iii) Daphnia + citrate-nAg + predator; and (iv) Daphnia only
33 g four different treatment combinations: (i) Daphnia + citrate-nAg; (ii) Daphnia + predator; (iii) Da
34 hnikowia bicuspidata) in a zooplankton host (Daphnia dentifera) among lakes.
35  experimental data using a zooplankton host (Daphnia dentifera) that consumes spores of a fungus (Met
36 ing a planktonic system (a zooplankton host, Daphnia dentifera, and its virulent fungal parasite, Met
37 apping 342 tentative orthologous gene pairs (Daphnia/Drosophila) into the Daphnia linkage map, we fac
38 ith a consumer-resource system of crustacean Daphnia eating algae, Nelson et al. suggest that mainten
39 Between 25 and 30 degrees C, both species of Daphnia experienced a precipitous drop in feeding rates,
40                        Our results show that Daphnia exposed to low levels of TNT presented hormetic
41      Vitamin B12 had a positive influence on Daphnia fitness and we provide evidence demonstrating th
42 llocation towards growth and reproduction in Daphnia found in lakes with anadromous alewife.
43           We reared replicate populations of Daphnia from all three lake types and quantified lifetim
44                                              Daphnia from anadromous lakes produced significantly mor
45 e number of reproductive bouts compared with Daphnia from lakes with landlocked and no alewife.
46 odied Daphnia species, Daphnia pulicaria and Daphnia galeata mendotae, were present.
47 ng cyanobacteria in the diet of experimental Daphnia galeata populations composed of eight genotypes.
48 an clearly be used to monitor changes in the Daphnia-generated fluid outflow on a different time scal
49           We suggest that the differences in Daphnia genetic diversity that they find for different e
50 ecome the anchor for the physical map of the Daphnia genome and will serve as a starting point for ma
51  review recent progress in selected areas of Daphnia genomics research.
52 n, pi(s), averaged 0.0136 for species in the Daphnia genus, and are slightly lower than most prior es
53 te (c/u), averaged 0.5255 for species of the Daphnia genus.
54                  The promoter regions of the Daphnia globin genes each contain numerous hypoxia respo
55 , however, warming resulted in a decrease in Daphnia grazing effectiveness.
56 aturated fatty acids known to be involved in Daphnia growth and reproduction.
57 i to t-POC-dominated diets greatly increased Daphnia growth and reproduction.
58      When offered alone, t-POC resulted in a Daphnia growth efficiency of 5 +/- 1%, whereas 100% Cryp
59                                     However, Daphnia growth rate was 3.5 times greater when fed high-
60               The keystone aquatic herbivore Daphnia has been studied for more than 150 years in the
61                                              Daphnia has recently received increased attention becaus
62                                 Past work on Daphnia has shown that the level of sexual recruitment (
63 ty of several waterflea species of the genus Daphnia have been found to be inducible defenses activat
64 e to specifically bind human, Drosophila, or Daphnia HIF complexes in vitro.
65                                              Daphnia HIF, bound to human HRE sequences, was detected
66 ration (C)) on the chronic toxicity of Cl to Daphnia in soft-water bioassays.
67 tapopulations of two species of water fleas (Daphnia) in the skerry archipelago of southern Finland.
68 vival test showed a significant mortality of Daphnia individuals in the presence of predators, with o
69                           When the herbivore Daphnia is added, coexistence is eliminated or greatly r
70 lts suggest that a salt-tolerant genotype of Daphnia is characterised by constitutively expressed gen
71 roximated by a chain (typically, those where Daphnia is the dominant herbivore), as predicted by food
72 ossing two genetically divergent lineages of Daphnia isolated from two Oregon populations.
73  (NaCl or CaCl2) did not affect the Cl LC50, Daphnia life history parameters, or the intrinsic rate o
74  amplified gene families are specific to the Daphnia lineage.
75 ous gene pairs (Daphnia/Drosophila) into the Daphnia linkage map, we facilitate future comparative pr
76 ics of the non-native cladoceran zooplankter Daphnia lumholtzi and a native congener Daphnia pulex in
77 ior to invasion by a non-native zooplankter, Daphnia lumholtzi.
78 zation were significantly overrepresented in Daphnia magna (DM) exposed to sublethal doses of presume
79 bly exceed acute toxicity concentrations for Daphnia magna .
80 the antibiotic trimethoprim on microbiota of Daphnia magna and concomitant changes in the host feedin
81 formed using ground beef and was verified in Daphnia magna and Lumbriculus variegatus .
82 ate-AgNPs, in comparison to dissolved Ag, in Daphnia magna and Lumbriculus variegatus; and (ii) inves
83 says, the immobilization of the invertebrate Daphnia magna and the bioluminescence inhibition of the
84 rics based on the most sensitive species and Daphnia magna as benchmark.
85 mulation of storage lipids in the crustacean Daphnia magna can be altered by a number of exogenous an
86                 Previous toxicity tests with Daphnia magna exposed to binary mixtures of Ni combined
87       It was found that at the LC50 level of Daphnia magna exposed to the nanoparticle suspensions, t
88 ity to represent lethal effects observed for Daphnia magna exposed to triphenyltin.
89 n polymerase chain reaction assays targeting Daphnia magna genes were calibrated to responses elicite
90 d strain-specific immunity in the crustacean Daphnia magna infected with the pathogenic bacteria Past
91                                              Daphnia magna is a bioindicator organism accepted by sev
92         Case studies on a Cu test pattern, a Daphnia magna model organism and a perlite biocatalyst s
93 gated the chronic toxicity to the water flea Daphnia magna of two HFFRs, aluminum diethylphosphinate
94 heir core structure and surface chemistry to Daphnia magna over a 21-day chronic exposure.
95 recently investigated in the microcrustacean Daphnia magna over a three-generation exposure (F0, F1,
96 ne reuptake inhibitor, on the life traits of Daphnia magna over two generations under environmentally
97                 We used the individual based Daphnia magna population model IDamP as a virtual labora
98 rse and representative sample of one natural Daphnia magna population that was exposed to copper and
99 take inhibitors (SSRIs) and 4-nonylphenol in Daphnia magna reproduction were studied in juveniles and
100 ian vegetation) and various phytoplankton on Daphnia magna somatic growth, reproduction, growth effic
101 ug L(-1) as total Ag) on the interactions of Daphnia magna Straus (as a prey) with the predatory drag
102                 A population experiment with Daphnia magna tested the hypothesis that short-term feed
103 x (branchiopod) genome and identify genes in Daphnia magna that are known to be required for the sele
104 that exposure of the freshwater invertebrate Daphnia magna to dietary Zn may selectively affect repro
105 ent with replicate laboratory populations of Daphnia magna to test this hypothesis.
106 chanisms underlying the hormetic response of Daphnia magna to the energetic trinitrotoluene (TNT).
107 gated the response of the nontarget organism Daphnia magna to waterborne DiPel ES, a globally used Bt
108 , maturation, reproduction, and survival) of Daphnia magna under surplus and reduced food availabilit
109  toxicity to the model freshwater crustacean Daphnia magna was characterized utilizing acute (48 h me
110                               The cladoceran Daphnia magna was used in two experiments that were cond
111 uction, and malformations of the zooplankter Daphnia magna were assessed.
112 epuration experiments for Gammarus pulex and Daphnia magna were conducted to quantitatively analyze b
113                                              Daphnia magna were exposed to TNT for 21 days, and a sig
114 onal variation in cyclically parthenogenetic Daphnia magna with respect to parasitic infection.
115              Condensate completely dissolved Daphnia magna within 24 h.
116 uring phytoplankton deficiency, zooplankton (Daphnia magna) can benefit from terrestrial particulate
117 sence of a less sensitive competing species (Daphnia magna).
118 we used a 15k oligonucleotide microarray for Daphnia magna, a freshwater crustacean and common indica
119  methylation patterns in the microcrustacean Daphnia magna, a model organism in ecotoxicology and ris
120  signalling in a crustacean, the branchiopod Daphnia magna, and show that it is required in neural st
121                             With the aquatic Daphnia magna, anthracene, chrysene, and benzo(a)pyrene
122 f metal mixtures (Ni, Zn, Cu, Cd, and Pb) to Daphnia magna, Ceriodaphnia dubia, and Hordeum vulgare w
123 s, carbon transfer between phytoplankton and Daphnia magna, D. magna mobility and growth, responded t
124 median acute effect concentration (EC50) for Daphnia magna, depending on the model specification and
125 dokirchneriella subcapitata, and a consumer, Daphnia magna, is affected by acute exposure of gamma ra
126 eshwater invertebrate-parasite system (host: Daphnia magna, parasite: Pasteuria ramosa), we quantifie
127 or different freshwater organisms, including Daphnia magna, rainbow trout and juvenile crayfish, and
128 nes that exist in the fresh-water crustacean Daphnia magna, several are individually induced by hypox
129                            In the water flea Daphnia magna, SSRIs increase offspring production in a
130 shwater invertebrates Ceriodaphnia dubia and Daphnia magna, suggesting that the aquatic toxicity is p
131 ign consisted of two developmental stages of Daphnia magna, two levels of nTiO2 (0 versus 2 mg/L) as
132 12 availability and methotrexate exposure on Daphnia magna, which we hypothesised should have an oppo
133       Using the natural host-parasite system Daphnia magna-Pasteuria ramosa, we performed experimenta
134 citrate-AgNPs) against a keystone crustacean Daphnia magna.
135 re known to increase offspring production in Daphnia magna.
136 early life stage zebrafish (Danio rerio) and Daphnia magna.
137 nd predation risk on the body composition of Daphnia magna.
138 e-history traits of a key aquatic herbivore, Daphnia magna.
139 e effects were explored using the cladoceran Daphnia magna.
140  of the algae Chlorella vulgaris and daphnid Daphnia magna.
141 d its transformation products to the daphnid Daphnia magna.
142  of nTiO2 and differing organic materials on Daphnia magna.
143 rmethrin, on the mortality of the crustacean Daphnia magna.
144 ns was assessed on the freshwater crustacean Daphnia magna.
145 e and xenobiotics on oxidative biomarkers in Daphnia magna.
146 s of the genus, this suggests that the genus Daphnia may be considerably younger than previously thou
147 les exceeded available diet, indicating that Daphnia may convert a part of their dietary carbohydrate
148                                              Daphnia MeHg assimilation efficiencies (approximately 95
149 icity in rapid adaptation of the zooplankton Daphnia melanica to novel fish predators.
150 ntal and vertical movements, indicating that Daphnia might have perceived a significant risk of preda
151 s estimates of the gene conversion rate from Daphnia mutation accumulation lines, we are able to age
152 ansion segment 43/e4 of the 18S rRNA gene in Daphnia obtusa have examined this variation in six indiv
153 ) Daphnia + citrate-nAg + predator; and (iv) Daphnia only (control).
154                  We also show that swarms of Daphnia plankton are a natural source of electrical nois
155 l stability and their associated patterns of Daphnia population structure.
156                                              Daphnia populations coexisting with recently introduced
157 that direct life history shifts in algae and Daphnia populations may occur as a result of exposure to
158          Epidemics grew larger in more dense Daphnia populations, but host density was unrelated to h
159 tical and empirical studies, particularly in Daphnia populations, have helped to establish that genet
160 able experiments were performed for two such Daphnia populations.
161 ombinations: (i) Daphnia + citrate-nAg; (ii) Daphnia + predator; (iii) Daphnia + citrate-nAg + predat
162  we take advantage of the recently published Daphnia pulex (branchiopod) genome and identify genes in
163 families responsive to Microcystis stress in Daphnia pulex .
164 ide variation in six protein-coding loci for Daphnia pulex and its congeners with particular emphasis
165 ions, growth and ingestion rates in juvenile Daphnia pulex fed either high (C:P = 139) or low-quality
166                  When exposing two different Daphnia pulex genotypes (a cadmium-sensitive and a cadmi
167 te and spectrum of mutations obtained in two Daphnia pulex genotypes via separate mutation-accumulati
168 kter Daphnia lumholtzi and a native congener Daphnia pulex in ambient temperature environments (contr
169 sis of 11 sexual and 11 asexual genotypes of Daphnia pulex indicates that current asexual lineages ar
170                     The cyclical parthenogen Daphnia pulex is a powerful model in which to address th
171                                              Daphnia pulex is a widely used toxicological model and i
172 es between the whole-genome sequences of two Daphnia pulex isolates.
173                          The microcrustacean Daphnia pulex provides a potentially powerful tool for i
174      Here, we studied clonal richness of the Daphnia pulex species complex in novel periglacial habit
175 ponds disable the ability of the water flea, Daphnia pulex to respond effectively to its predator, la
176 e describe the first genetic linkage map for Daphnia pulex using 185 microsatellite markers, includin
177 karyotic organisms, Drosophila melanogaster, Daphnia pulex, Ciona intestinalis and Strongylocentrotus
178              Paland and Lynch showed that in Daphnia pulex, the ratio of amino acid replacement to si
179 fR protein subunits Met and SRC, cloned from Daphnia pulex, were fused to the fluorophore, mAmetrine
180 ribe the draft genome of the microcrustacean Daphnia pulex, which is only 200 megabases and contains
181 enorhabditis elegans and the microcrustacean Daphnia pulex.
182 an in sexual lineages of the microcrustacean Daphnia pulex.
183 tic populations of the cladoceran crustacean Daphnia pulex.
184 l habitats out of which 61 were colonized by Daphnia pulex.
185 ther lakes, decreasing biomass of the grazer Daphnia pulicaria and causing a decline in water clarity
186 onditions when large-bodied Daphnia species, Daphnia pulicaria and Daphnia galeata mendotae, were pre
187                                              Daphnia pulicaria performed significantly better at cold
188    In the present study, on a permanent lake Daphnia pulicaria population, sexual reproduction result
189 gle Nucleotide Polymorphic (SNP) markers for Daphnia pulicaria using the reduction in genomic complex
190  generation time, on deleterious mutation in Daphnia pulicaria, a cyclically parthenogenic aquatic mi
191 mant eggs of the keystone aquatic herbivore, Daphnia pulicaria, suggested no change for c. 1500 years
192 es that introgression from a sister species, Daphnia pulicaria, underlies the origin of the asexual p
193 tructure of the keystone zooplankton grazer, Daphnia pulicaria, using dormant eggs extracted from sed
194 four populations of the cyclical parthenogen Daphnia pulicaria, which vary predictably in their incid
195  small-bodied Daphnia ambigua and the larger Daphnia pulicaria.
196  effective supply of P is greatly reduced as Daphnia rapidly recycles N.
197                                              Daphnia reproduction was slightly enhanced by approximat
198            First, resources should stimulate Daphnia reproduction, potentially elevating host density
199 ever, with citrate-nAg + predator treatment, Daphnia response did not differ from control in the vert
200 tion of organic contaminants in sediments in Daphnia resting eggs (ephippia).
201                         More than a third of Daphnia's genes have no detectable homologs in any other
202 the obesogenic disruption in mammals, alters Daphnia's growth and reproductive investment.
203                 Overall, our results suggest Daphnia selectively allocate phytoplankton-derived POC a
204                                      Exposed Daphnia showed a reduced body size and severe alteration
205              A paleoecological assessment of Daphnia shows that this sentinel zooplankter has not yet
206 was examined in standard OECD media used for Daphnia sp. acute and chronic tests (in the absence of D
207 generally followed expectations, making both Daphnia species more effective grazers, with the increas
208 collection of D. pulex isolates and outgroup Daphnia species shows that most polymorphisms are a cons
209 creases the stability of the carapace in two Daphnia species up to 350%.
210  hypereutrophic conditions when large-bodied Daphnia species, Daphnia pulicaria and Daphnia galeata m
211                                              Daphnia-specific genes, including many additional loci w
212                                 We estimated Daphnia steady-state MeHg concentrations, using a biokin
213 a wide variety of new genomic resources, the Daphnia system is quickly becoming a promising new avenu
214 ol for future population genomics surveys in Daphnia targeting informative regions related to physiol
215          Steady-state MeHg concentrations in Daphnia that consumed high-quality algae were one-third
216 d high-quality algae were one-third those of Daphnia that consumed low-quality algae due to higher gr
217 we describe a gut parasite of the crustacean Daphnia that despite having remarkable morphological sim
218                                              Daphnia that obtained 80% of their available food from t
219 ow in mutation-accumulation lines of asexual Daphnia that the rate of loss of nucleotide heterozygosi
220 erability of the smaller juvenile instars of Daphnia, the stages most susceptible to Chaoborus predat
221 of two species of cyclically parthenogenetic Daphnia to assess the effect of partial asexual reproduc
222 lighted differential methylation patterns in Daphnia upon exposure to Microcystis primarily in exonic
223 d by experimental studies of the zooplankton Daphnia, we model foraging animals as "agents" moving in
224 the vertical migration test, suggesting that Daphnia were unable to detect the presence of predator w
225 acterial blooms, especially species of genus Daphnia, which are key-species in lake ecosystems.
226               The planktonic microcrustacean Daphnia, which has long been an important system for eco
227 etapopulations of two species of waterfleas (Daphnia) with the aim to understand how these dynamics i

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