Greenfall Links Groundwater to Aboveground Food Webs in Desert River Floodplains

Groundwater makes up nearly 99% of unfrozen freshwater worldwide and sustains riparian trees rooted in shallow aquifers, especially in arid and semiarid climates. The goal of this paper is to root animals in the regional water cycle by quantifying the significance of groundwater to riparian animals. We focused our efforts on the cricket, Gryllus alogus: a common primary consumer found in floodplain forests along the San Pedro River, in southeast Arizona, USA. Cottonwood trees make groundwater available to G. alogus as dislodged, groundwater-laden leaves (greenfall). We hypothesized that groundwater fluxes mediated by greenfall sustain G. allogus through the prolonged dry season and link these aboveground consumers to belowground aquifers. To test this hypothesis, we first characterized gradients in absolute humidity (air) and water stress in field-collected G. alogus. Absolute humidity declined with distance from river across wide stands of floodplain cottonwood forest during the dry season, but not during the rainy season. Similarly, G. alogus body water content declined along this gradient. Second, we measured evaporative water loss (EWL) by field-captured G. alogus in the laboratory at temperatures bracketing field conditions. EWL ranged from 0.05 ± 0.009 g·individual-1·d-1 0.13 ± 0.03 g·individual-1·d-1 (mean ± SD, at 30° and 40°C, respectively). These daily losses are high, but still less than the water content of a single cottonwood leaf (0.296 ± 0.124 g H2O/leaf). Third, we designed field experiments to quantify the relative dependence of G. alogus on greenfall. G. alogus more frequently consumed greenfall than various controls consisting of dried leaves. This preference occurred in distal habitats and during the dry season, but not proximal to the river or in the rainy season. Finally, we compared estimated daily water fluxes via greenfall to (1) estimates of water demand of the entire G. alogus population at our field site, and (2) reports of cottonwood transpiration and San Pedro River base flow from other authors. By our estimates, groundwater fluxes via greenfall sustain G. alogus populations despite their trivial magnitude compared to stream discharge and cottonwood transpiration. Primary consumers in turn provide dietary water to higher trophic levels (e.g., abundant and speciose birds in the region) through trophic pathways, thereby fueling secondary production from the bottom up. Thus, riparian trees root animals in the regional water cycle

Comparative feeding ecology of shortfin mako, blue and thresher sharks in the California Current.

Abstract This study describes the feeding ecology of three pelagic shark species in the California Current: shortfin mako (Isurus oxyrinchus); blue (Prionace glauca); and thresher (Alopias vulpinus) sharks. Stomach contents of sharks collected from 2002 to 2008 were identified to the lowest taxonomic level and analyzed using univariate and multivariate methods. Of 330 mako sharks sampled (53 to 248 cm fork length [FL]), 238 stomachs contained 42 prey taxa, with jumbo squid (Dosidicus gigas) and Pacific saury (Cololabis saira) representing the most important prey based on the geometric index of importance (GII). In addition, 158 blue sharks were sampled (76 to 248 cm FL) and 114 stomachs contained 38 prey taxa, with jumbo and Gonatus spp. squids representing the most important prey. Lastly, 225 thresher sharks were sampled (108 to 228 cm FL) and 157 stomachs contained 18 prey taxa with northern anchovy (Engraulis mordax) and Pacific sardine (Sardinops sagax) identified as the most important prey. Overall, mako sharks had the most diverse diet based upon Simpson's diversity index (1/D) (8.43±1.16), feeding on many species of teleosts and cephalopods, followed by blue sharks (6.20±2.11) which consumed a wide range of prey (primarily cephalopods), while thresher sharks were most specialized (2.62±0.34), feeding primarily on coastal pelagic teleosts. Dietary overlap was lowest between blue and thresher sharks (Sørensen similarity index00.321 and Simplified Morisita Horn index0 0.006), and seasonal variability in diet was greatest for blue sharks (Simplified Morisita Horn index0 0.260, Analysis of Similarity (ANOSIM) p<0.001). In addition, size class, and subregion were significant factors that affected diet of each species differently (ANOSIM p<0.001). Despite similarities in life history characteristics and spatial and temporal overlap in habitat, diets of these three common shark species are distinct in the California Current

Comparative feeding ecology of shortfin mako, blue and thresher sharks in the California Current.

Abstract This study describes the feeding ecology of three pelagic shark species in the California Current: shortfin mako (Isurus oxyrinchus); blue (Prionace glauca); and thresher (Alopias vulpinus) sharks. Stomach contents of sharks collected from 2002 to 2008 were identified to the lowest taxonomic level and analyzed using univariate and multivariate methods. Of 330 mako sharks sampled (53 to 248 cm fork length [FL]), 238 stomachs contained 42 prey taxa, with jumbo squid (Dosidicus gigas) and Pacific saury (Cololabis saira) representing the most important prey based on the geometric index of importance (GII). In addition, 158 blue sharks were sampled (76 to 248 cm FL) and 114 stomachs contained 38 prey taxa, with jumbo and Gonatus spp. squids representing the most important prey. Lastly, 225 thresher sharks were sampled (108 to 228 cm FL) and 157 stomachs contained 18 prey taxa with northern anchovy (Engraulis mordax) and Pacific sardine (Sardinops sagax) identified as the most important prey. Overall, mako sharks had the most diverse diet based upon Simpson's diversity index (1/D) (8.43±1.16), feeding on many species of teleosts and cephalopods, followed by blue sharks (6.20±2.11) which consumed a wide range of prey (primarily cephalopods), while thresher sharks were most specialized (2.62±0.34), feeding primarily on coastal pelagic teleosts. Dietary overlap was lowest between blue and thresher sharks (Sørensen similarity index00.321 and Simplified Morisita Horn index0 0.006), and seasonal variability in diet was greatest for blue sharks (Simplified Morisita Horn index0 0.260, Analysis of Similarity (ANOSIM) p<0.001). In addition, size class, and subregion were significant factors that affected diet of each species differently (ANOSIM p<0.001). Despite similarities in life history characteristics and spatial and temporal overlap in habitat, diets of these three common shark species are distinct in the California Current

Multitaxonomic Diversity Patterns along a Desert Riparian–Upland Gradient

Riparian areas are noted for their high biodiversity, but this has rarely been tested across a wide range of taxonomic groups. We set out to describe species richness, species abundance, and community similarity patterns for 11 taxonomic groups (forbs & grasses, shrubs, trees, solpugids, spiders, scarab beetles, butterflies, lizards, birds, rodents, and mammalian carnivores) individually and for all groups combined along a riparian–upland gradient in semiarid southeastern Arizona, USA. Additionally, we assessed whether biological characteristics could explain variation in diversity along the gradient using five traits (trophic level, body size, life span, thermoregulatory mechanism, and taxonomic affiliation). At the level of individual groups diversity patterns varied along the gradient, with some having greater richness and/or abundance in riparian zones whereas others were more diverse and/or abundant in upland zones. Across all taxa combined, riparian zones contained significantly more species than the uplands. Community similarity between riparian and upland zones was low, and beta diversity was significantly greater than expected for most taxonomic groups, though biological traits explained little variance in diversity along the gradient. These results indicate heterogeneity amongst taxa in how they respond to the factors that structure ecological communities in riparian landscapes. Nevertheless, across taxonomic groups the overall pattern is one of greater species richness and abundance in riparian zones, coupled with a distinct suite of species

Appendix B. The O-ring statistic, g12(r), vs. time, Moran scatterplots, and Moran scatterplot maps.

The O-ring statistic, g12(r), vs. time, Moran scatterplots, and Moran scatterplot maps

Appendix A. Description of the bycatch, target catch, and fishing effort.

Description of the bycatch, target catch, and fishing effort

Conservation Status of North American Birds in the Face of Future Climate Change

<div><p>Human-induced climate change is increasingly recognized as a fundamental driver of biological processes and patterns. Historic climate change is known to have caused shifts in the geographic ranges of many taxa and future climate change is expected to result in even greater redistributions of species. As a result, predicting the impact of climate change on future patterns of biodiversity will greatly aid conservation planning. Using the North American Breeding Bird Survey and Audubon Christmas Bird Count, two of the most comprehensive continental datasets of vertebrates in the world, and correlative distribution modeling, we assessed geographic range shifts for 588 North American bird species during both the breeding and non-breeding seasons under a range of future emission scenarios (SRES A2, A1B, B2) through the end of the century. Here we show that 314 species (53%) are projected to lose more than half of their current geographic range across three scenarios of climate change through the end of the century. For 126 species, loss occurs without concomitant range expansion; whereas for 188 species, loss is coupled with potential to colonize new replacement range. We found no strong associations between projected climate sensitivities and existing conservation prioritizations. Moreover, species responses were not clearly associated with habitat affinities, migration strategies, or climate change scenarios. Our results demonstrate the need to include climate sensitivity into current conservation planning and to develop adaptive management strategies that accommodate shrinking and shifting geographic ranges. The persistence of many North American birds will depend on their ability to colonize climatically suitable areas outside of current ranges and management actions that target climate adaptation.</p></div

Stability and change in geographic range size in the breeding and non-breeding season in relation to migratory groups.

<p><b>(a)</b> Change in current geographic range size (year 2000) by 2080 (SRES A2) grouped by migratory behavior (<a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0135350#pone.0135350.s005" target="_blank">S5</a> and <a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0135350#pone.0135350.s006" target="_blank">S6</a> Appendices). <b>(b)</b> Proportional change in range size by 2080 (SRES A2) grouped by migratory behavior (<a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0135350#pone.0135350.s005" target="_blank">S5</a> and <a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0135350#pone.0135350.s006" target="_blank">S6</a> Appendices).</p

Impacts of future climate change on geographic ranges of North American bird species (<i>n</i> = 588) by 2080 during the breeding (top row) and non-breeding season (bottom row) under SRES A2 scenario.

<p>Changes in total number of species by 2080 due to shifting ranges relative to year 2000 baseline showing potential <b>(a)</b> species gain or <b>(b)</b> loss. <b>(c)</b> Bray-Curtis dissimilarity showing turnover in species composition of local communities.</p

Relationship between current range stability (year 2000 range remaining in 2080) and potential range expansion (proportional to current range size) under SRES A2 scenario by year 2080.

<p><b>(a)</b> Two-dimensional density plot (10% contours) of North American bird species showing current range stability versus potential range expansion for <b>(b)</b> breeding (<i>n</i> = 475) with three distinct groups: (i) current geographic range decreases with little to no expansion potential; (ii) current geographic range shifts to other parts of North America; and, (iii) current geographic range remains stable and, in some cases, expands, and <b>(c)</b> non-breeding seasons (<i>n</i> = 503). Species with expansion values >1.0 were truncated to 1.0 to appear on plots.</p