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Connections among ecosystems and their components are critical to maintaining ecological functions and benefits in human-modified landscapes, including urban areas. However, the literature on connectivity and ecosystem services has been limited by inconsistent terminology and methods, and largely omits human access to nature and its benefits as a form of connectivity. In this paper, we build upon previous research and theory to define distinct categories of connectivity, considering both ecological and social dimensions, and identify ecosystem services that are supported by them. We reviewed the literature to determine socio–ecological benefits that depend on the categories of connectivity. We identified four distinct but interrelated categories of connectivity: landscape, habitat, geophysical, and eco-social connectivity. Each connectivity category directly or indirectly supports many ecosystem services. There are overlaps, conflicts, and synergies among connectivity categories and their associated services and disservices. Identifying the services that arise from these four categories of connectivity, and how they interact, can help build a common understanding of the value of connectivity to maximize its benefits, improve understanding of complex socio–ecological systems across disciplines, and develop more holistic, socially equitable decision-making processes, especially in urban landscapes.

Adaptation across environmental gradients has been demonstrated in numerous systems with extensive dispersal, despite high gene flow and consequently low genetic structure. The speed and mechanisms by which such adaptation occurs remain poorly resolved, but are critical to understanding species spread and persistence in a changing world. Here, we investigate these mechanisms in the European green crab Carcinus maenas, a globally distributed invader. We focus on a northwestern Pacific population that spread across12 degrees of latitude in 10 years from a single source, following its introduction35 years ago. Using six locations spanning1500 km, we examine genetic structure using 9376 single nucleotide polymorphisms (SNPs). We find high connectivity among five locations, with significant structure between these locations and an enclosed lagoon with limited connectivity to the coast. Among the five highly connected locations, the only structure observed was a cline driven by a handful of SNPs strongly associated with latitude and winter temperature. These SNPs are almost exclusively found in a large cluster of genes in strong linkage disequilibrium that was previously identified as a candidate for cold tolerance adaptation in this species. This region may represent a balanced polymorphism that evolved to promote rapid adaptation in variable environments despite high gene flow, and which now contributes to successful invasion and spread in a novel environment. This research suggests an answer to the paradox of genetically depauperate yet successful invaders: populations may be able to adapt via a few variants of large effect despite low overall diversity.

The establishment of non-indigenous species is influenced both by species traits and the biotic interactions that create resistance to or facilitate invasion. Predation, for example, creates resistance to non-indigenous ascidians in benthic habitats. Daytime surveys of fouling communities on floating docks in the Charleston Marina, Oregon, USA in August 2014 revealed that the indigenous ascidian Distapla occidentalis was present at all sites and was being consumed by the flatworm Eurylepta leoparda and the nudibranch Hermissenda crassicornis. In contrast, the non-indigenous Botrylloides violaceus and Botryllus schlosseri were present at fewer sites and lacked signs of predation. Parallel surveys in July 2015 again revealed predators found on docks were eating the indigenous ascidian. Examination of surrounding intertidal habitats revealed the dominant predators were the hermit crab Pagurus granosimanus and shore crab Hemigrapsus oregonensis, species not found in the marina fouling community. Feeding assays with the four predators and the ascidians showed that the flatworm specialized on the indigenous D. occidentalis, eating it almost 50 times faster than the NIS, which it did not consume. The nudibranch and shore crab mainly fed on D. occidentalis as well, consuming it two to four times faster than the NIS. In contrast, the benthic hermit crab mainly fed on the non-indigenous ascidian, feeding on it almost three times faster than it ate D. occidentalis. Hence, the non-indigenous ascidian likely faced reduced predation pressure in the marina fouling communities, increasing invasion risk. The study also examined several aspects of ascidian palatability, which showed that predator feeding was affected by differences in tunic structure. The study suggests that the different predators in the fouling and benthic communities in this marina have a role in the invasion of ascidians.

People in urban and rural areas are planting habitat patches for pollinators in response to growing public awareness of the risks of pollinator declines; yet research rarely has been undertaken to inform the composition of such patches. Determining which key functional plant traits to prioritize and how plant-pollinator interaction dynamics operate in these small-scale, fragmented patches is critical to ensuring the efficacy of pollinator restoration efforts across landscapes. We established small-scale (2.5 m diameter) experimental patches and manipulated plant diversity and resource level (nectar) to determine the effects on pollinator abundance, pollinator diversity, and plant-pollinator facilitation-competition dynamics. Our results showed that in small-scale habitat, plant diversity and resource availability significantly affected the abundance and diversity of pollinating insects. Specifically, the treatments that contained high-resource plant species increased pollinator abundance and diversity the most. Plant diversity increased pollinator diversity and abundance only in the absence of high-resource plants. Pollination facilitation was observed in high-resource treatments, but varied among plant species. Competition for pollinators was observed in high-diversity treatments but did not affect seed set for high-resource plants in any of the treatments. Our results suggest that managers or landowners planting small-scale pollinator habitat should prioritize including species with high nectar production, and secondarily, a diverse mix of species if space and resources allow. The protocols we used to monitor pollinators can be used by community science observers with limited training, expanding the potential for assessment of future pollinator habitat restoration projects. Shared research identifying features critical to effective restoration will help conserve plant-pollinator mutualisms across landscapes.

As biological invasions continue to increase globally, eradication programs have been undertaken at significant cost, often without consideration of relevant ecological theory. Theoretical fisheries models have shown that harvest can actually increase the equilibrium size of a population, and uncontrolled studies and anecdotal reports have documented population increases in response to invasive species removal (akin to fisheries harvest). Both findings may be driven by high levels of juvenile survival associated with low adult abundance, often referred to as overcompensation. Here we show that in a coastal marine ecosystem, an eradication program resulted in stage-specific overcompensation and a 30-fold, single-year increase in the population of an introduced predator. Data collected concurrently from four adjacent regional bays without eradication efforts showed no similar population increase, indicating a local and not a regional increase. Specifically, the eradication program had inadvertently reduced the control of recruitment by adults via cannibalism, thereby facilitating the population explosion. Mesocosm experiments confirmed that adult cannibalism of recruits was size-dependent and could control recruitment. Genomic data show substantial isolation of this population and implicate internal population dynamics for the increase, rather than recruitment from other locations. More broadly, this controlled experimental demonstration of stage-specific overcompensation in an aquatic system provides an important cautionary message for eradication efforts of species with limited connectivity and similar life histories.

Predators exert considerable top‐down pressure on ecosystems by directly consuming prey or indirectly influencing their foraging behaviors and habitat use. Prey is, therefore, forced to balance predation risk with resource reward. A growing list of anthropogenic stressors such as rising temperatures and ocean acidification has been shown to influence prey risk behaviors and subsequently alter important ecosystem processes. Yet, limited attention has been paid to the effects of chronic pharmaceutical exposure on risk behavior or as an ecological stressor, despite widespread detection and persistence of these contaminants in aquatic environments. In the laboratory, we simulated estuarine conditions of the shore crab, Hemigrapsus oregonensis, and investigated whether chronic exposure (60 days) to field‐detected concentrations (0, 3, and 30 ng/L) of the antidepressant fluoxetine affected diurnal and nocturnal risk behaviors in the presence of a predator, Cancer productus. We found that exposure to fluoxetine influenced both diurnal and nocturnal prey risk behaviors by increasing foraging and locomotor activity in the presence of predators, particularly during the day when these crabs normally stay hidden. Crabs exposed to fluoxetine were also more aggressive, with a higher frequency of agonistic interactions and increased mortality due to conflicts with conspecifics. These results suggest that exposure to field‐detected concentrations of fluoxetine may alter the trade‐off between resource acquisition and predation risk among crabs in estuaries. This fills an important data gap, highlighting how intra‐ and interspecific behaviors are altered by exposure to field concentrations of pharmaceuticals; such data more explicitly identify potential ecological impacts of emerging contaminants on aquatic ecosystems and can aid water quality management.

Whereas roads that bisect habitat are known to decrease population size through animal-vehicle collisions or interruption of key life history events, it is not always obvious how to reduce such impacts, especially for flying organisms. We needed a quick, cost-efficient and effective way to determine how best to decrease vehicle-caused mortality while maintaining habitat connectivity for the federally listed Oregon silverspot butterfly, Speyeria zerene hippolyta. Therefore, we gathered targeted ecological information that informed selection of a mitigation option prior to implementation. We sampled butterfly behavior and environmental conditions along a highway and conducted a small-scale experiment along a decommissioned road corridor used by these butterflies. Using our findings, we recommended vegetation management and helped managers eliminate options they were considering that would be ineffective such as increasing shade or wind in the road, and installing fencing or hedgerows aimed at directing flight above traffic. This quick and inexpensive approach of using ecological observations and small-scale experiments to evaluate the likely success of each available mitigation option can be used to determine effective, species-specific solutions for reducing traffic impacts on pollinators and other small, flying organisms of conservation concern.

Barriers to animal movement can isolate populations, impacting their genetic diversity, susceptibility to disease, and access to resources. Barriers to movement may be caused by artificial light, which is known to disrupt bird, sea turtle, and bat behavior, but few studies have experimentally investigated the effects of artificial light on movement for a suite of terrestrial vertebrates. Therefore, we studied the effect of ecological light pollution on animal usage of a bridge under-road passage structure. On a weekly basis, sections of the structure were subjected to different light treatments including no light added, followed by a Reference period when lights were off in all the structure sections. Sand track data revealed use by 23 mammals, birds, reptiles and amphibians, nine of which had > 30 tracks for species-level analysis. Columbia black-tailed deer (Odocoileus hemionus columbianus) traversed under unlit bridge sections much less when neighboring sections were lit compared to when none were, suggesting avoidance due to any nearby presence of artificial light. Similarly, deer mouse (Peromyscus maniculatus) and opossum (Didelphis virginiana) track paths were less frequent in the lit sections than the ambient. Crossing was correlated with temporal or spatial factors but not light for three of the other species. These findings suggest that artificial light may be reducing habitat connectivity for some species though not providing a strong barrier for others. Such information is needed to inform mitigation of habitat fragmentation in the face of expanding urbanization.

Populations that span a large geographic range often experience a thermal gradient that can differentially affect the phenotypic response of individuals across the population. Variation in temperature has been shown to affect the final adult size of ectotherms, which is referred to as the temperature–size rule for ectotherms. Body size is a fundamentally important trait, as it can impact physiological performance, fecundity, longevity, and macroecological patterns. Hence, temperature may affect body size across a range, which can in turn influence maintenance of populations and ecological interactions. Here, we test whether biogeographic differences in size (carapace width) exist for a recent invasion of the non-native European green crab, Carcinus maenas, along the west coast of North America. We assembled trapping and temperature data collected from 10 sites along the western North American coast over a 5-year period. We also conducted a literature review of C. maenas size across their native range. Our results indicate that adult body size shows negative correlation with environmental temperature in both the native and invaded ranges, conforming to the temperature–size rule for ectotherms. Given the short time since colonization and lack of evident genetic structure across the invasive range, it may be that phenotypic plasticity in response to environmental temperature is driving this relationship. Forces that shape the phenotypic trajectory of species may play an important role in both invasion dynamics and subsequent ecological impacts.

Estuarine intertidal habitats are heterogeneous, therefore migratory shorebirds are expected to forage in microhabitats where they can maximize their energy intake. Identifying proximate factors that migratory shorebirds use to accept or reject a particular habitat patch will help land managers make conservation and restoration decisions that provide the greatest benefits to shorebird populations during migration, a period of intense energy usage. We examined whether small semipermanent tidal channels were preferentially used by foraging Western Sandpipers (Calidris mauri) and Dunlins (C. alpina) during a spring migratory stopover in Bandon Marsh, an Oregon, USA, estuary. Further, we tested alternative hypotheses about how channels might be beneficial to shorebirds by examining infauna abundance, composition, and depth alongside channels compared with that in open mudflats. The densities of Western Sandpipers and Dunlins were at least 4 times higher along channels than in open mudflat habitats. I...

Increases in temperature associated with global climate change are predicted to elicit drastic changes, especially to marine and freshwater ecosystems. Even small changes in water temperature (1–2 °C) may alter rates of biological activity, with concomitant effects to communities and ecosystems. The biological erosion of marine habitats and structures is a rarely considered yet important activity that is likely to be influenced by changing ocean temperatures. We conducted an experiment to test how seawater temperature affects erosion by a non-native crustacean (Sphaeroma quoianum). Aquaria were maintained at one of thirteen temperatures (7.5 °C–25.2 °C). In each aquarium, twenty isopods were encaged with an expanded polystyrene foam block (800 ml) and left to burrow. Polystyrene floats under docks are often damaged by isopods in the field. After two months, isopods created the longest burrows in the moderate seawater temperatures (13.8 °C–18.3 °C); these temperatures were 1.1–5.6 °C higher than the mean ambient temperatures whence they came. Shorter burrows were observed for the coldest (7.5 °C) and warmest seawater treatments (25.2 °C). These results indicate that increasing seawater temperatures can exacerbate the bioerosive effects of non-native S. quoianum until a threshold, after which the impacts diminish. Because ocean temperatures are predicted to increase 1.5–2.6 °C in the next 90 years, our data suggest erosion by this non-native crustacean will increase 14.7–37.6% in Coos Bay/South Slough, Oregon (where isopods were collected). However, other invaded bays on the Pacific coast of North America may also experience mean increases of biological erosion of 6.6–29.8%. Since biological activity is tightly coupled with temperature in many species, we hypothesize that the biological erosion rates of other erosive species will also increase with rising water temperatures affecting marine habitats, communities, and structures.

Physiological studies have long been utilized to understand the role of environmental temperature in the distribution of native organisms within marine communities. For the invasive crab Carcinus maenas, temperature has been implicated as the main predictor of establishment success across temperate regions. Therefore, we determined whether the lower temperature tolerances of this non-native crab would restrict it from spreading farther poleward from a relatively new recipient environment. Cold tolerance capacity was determined in the laboratory by holding crabs sampled from Vancouver Island, British Columbia (BC)—near the present northern limit for the northeast Pacific metapopulation to an overwintering thermal profile generated from Sitka, Alaska, USA. These crabs were physiologically capable of overwintering north of their present range boundary. The cellular response to cold stress was investigated using two functional categories of the cellular stress response. We measured cyclin D1, a cell-cycle regulator, and Hsp70, a protein chaperone, after laboratory acclimation and acute cold stress on two populations of C. maenas from the west coast of North America that have disparate thermal histories (crabs sampled from CA or BC). We found site-specific differential expression of cyclin D1 after cold acclimation and cold shock, perhaps affecting invasion capacity in this species. Determining what physiological mechanisms are in place with respect to thermal tolerance and preference can give insight into what makes an invasive organism successful and aid in predicting probable distribution of such species within a new environment.

Roads, while central to the function of human society, create barriers to animal movement through collisions and habitat fragmentation. Barriers to animal movement affect the evolution and trajectory of populations. Investigators have attempted to use traffic volume, the number of vehicles passing a point on a road segment, to predict effects to wildlife populations approximately linearly and along taxonomic lines; however, taxonomic groupings cannot provide sound predictions because closely related species often respond differently. We assess the role of wildlife behavioral responses to traffic volume as a tool to predict barrier effects from vehicle‐caused mortality and avoidance, to provide an early warning system that recognizes traffic volume as a trigger for mitigation, and to better interpret roadkill data. We propose four categories of behavioral response based on the perceived danger to traffic: Nonresponders, Pausers, Speeders, and Avoiders. Nonresponders attempt to cross highways regardless of traffic volume. Pausers stop in the face of danger so have a low probability of successful crossing when traffic volume increases. Hence, highway barrier effects are primarily due to mortality for Nonresponders and Pausers at high traffic volumes. Speeders run away from danger but are unable to do so successfully as traffic volume increases. At moderate to high volume, Speeders are repelled by traffic danger. Avoiders face lower mortality than other categories because they begin to avoid traffic at relatively low traffic volumes. Hence, avoidance causes barrier effects more than mortality for Speeders and Avoiders even at relatively moderate traffic volumes. By considering a species’ risk‐avoidance response to traffic, managers can make more appropriate and timely decisions to mitigate effects before populations decline or become locally extinct.

For marine ectotherms, environmental temperature plays an important role in helping to determine biogeographical distribu tions. Understanding the impacts that temperature can have on organismal function can lead to insights into the nature of adaptive variation in thermotolerance. This approach has been widely used to understand the spatial distribution of related species within the context of evolutionary time scales. Here, we measured the upper lethal thermal threshold of the invasive European green crab, Carcinus maenas (Linnaeus, 1758), sampled from two populations from the southern and northern limits of its recipient range on the west coast of North America: Sea Drift Lagoon, Stinson Beach, California (CA), and Pipestem Inlet, Vancouver Island, British Columbia (BC). These two populations differ in their natural thermal regimes; sea surface temperatures near the southern, CA population range from ~ 23 °C to ~ 11 °C while temperatures near the northern population in BC range from ~ 14 °C to ~ 6 °C during summer and winter, respectively. We demonstrate that after laboratory acclimation to 6 °C or 23 °C, the CA group had a significantly higher mean critical thermal maximum (CTmax) than its northern counterpart, in both acclimation groups. After acclimation to 6 °C, the CA group displayed a mean CTmax of 34.7 °C whereas the mean CTmax of the BC group was 31.7 °C. In the 23 °C acclimation groups, mean CTmax was 36.2 °C in the CA population and 35.5 °C in the BC one. To establish whether these differences in whole-organism thermotolerance were manifested at the molecular scale, levels of the inducible stress protein, heat shock protein 70 (Hsp70), were quantified in the chelae of the crabs used in the CTmax assay, at each individual's time-of-death. In the 6 °C acclimation comparison, the CA population had significantly greater Hsp70 levels than the BC population. No difference in Hsp70 levels was observed between the 23 °C acclimation groups. In a separate experiment, collection site-specific differences were found in the thermal threshold for induction of Hsp70 in isolated chelae tissue. The two populations also differed morphologically. Significant differences in carapace widths (CW) were measured for adult male and female green crabs from the two populations, sampled during 2008–2009. Observable divergences in both morphology and in physiological responses to heat stress have occurred within the relatively recent time span (~ 20 years) of the invasion of the European green crab on the west coast of North America and it is possible that a large, northern cold-water phenotype may have already arisen.

Despite the importance of invasions, few studies have explored their long-term conse­ quences in marine systems or examined multiple types of population-level effects. Initial effects, however, may not persist over longer time frames; effects have been shown to wane in freshwater systems. We combined 14 yr of field surveys (1993 to 2006) with manipulative experiments to exam­ ine the potential for multiple effects of a nonindigenous crab Carcinus maenas on the native shore crab Hemigrapsus oregonensis over time in central California. H. oregonensis abundance was nega­ tively correlated with C. maenas abundance. However, H. oregonensis abundance rebounded to pre­ invasion levels once C. maenas numbers declined. Other measured changes include a marked decrease in H. oregonensis body size and an increase in the proportion of H. oregonensis in the high intertidal zone since the arrival of C. maenas. These changes in body size and tidal distribution per­ sisted nearly a decade beyond the peak abundance of C. maenas and after H. oregonensis numbers rebounded. Observed changes in the distribution of the H. oregonensis population correspond to shifts in C. maenas abundance, and experiments support a causal relationship. Stepwise regression suggests a complex and possibly nonlinear relationship between predictor variables and H. orego­ nensis size and distribution. Overall, our data indicate strong perSistent effects on multiple attributes, with a lag in recovery with declining invader abundance, underSCOring the potential for long-term effects that are decoupled from year-to-year invasion dynamics.

Introduced species interact both directly and indirectly with native species. We examine interactions between the introduced New Zealand mud snail (Potamopyrgus antipodarum) and native estuarine invertebrates and predators through experiments and field studies. A widely held management concern is that when P. antipodarum, which has low nutritional value, becomes abundant, it replaces nutritious prey in fish diets. We tested two key components of this view: (1) that fish consume, but get little direct nutritional value from P. antipodarum; and (2) that P. antipodarum has an indirect negative effect on fish by reducing the energy derived from native prey. We also examined predation by the native signal crayfish, Pacifastacus leniusculus. Laboratory feeding trials showed that both crayfish and fish consume P. antipodarum, a direct effect. Crayfish consumed and successfully digested higher numbers of snails than did fish [Pacific staghorn sculpin (Leptocottus armatus), three spine stickleback (Gasterosteus aculeatus), and juvenile starry flounder (Platicthys stellatus)]. P. antipodarum occurred at low frequencies in the stomachs of wild-caught fish. More interesting were the indirect effects of this invader, which ran counter to predictions. P. antipodarum presence was associated with no change or an increase in the amount of energy derived from native prey by predators. The presence of P. antipodarum also led to increased consumption of and preference for the native amphipod Americorophium salmonis over the native isopod Gnorimosphaeroma insulare. This is an example of short-term, asymmetric, apparent competition, in which the presence of one prey species (snails) increases predation on another prey species (the amphipod). Electronic supplementary material The online version of this article (doi:10.1007/s00442-011-1962-8) contains supplementary material, which is available to authorized users.

Lateral erosion of saltmarshes is affected by many abiotic and biotic factors. While abiotic factors are typically regarded as primary drivers of erosion, biotic influences such as burrow- ing or bioturbating taxa can also extensively modify the physical structure of this marine habitat. Many estuaries on the Pacific coast of North America have been invaded by populations of the burrowing non-native isopod Sphaeroma quoianum, which are thought to exacerbate the erosion of saltmarshes. We conducted a mensurative experiment to examine the relationship between popula- tions of S. quoianum and lateral erosion rate of saltmarshes in Coos Bay, Oregon, USA. After 1 yr, we measured higher lateral erosion rates, more undercutting, and higher numbers of calved and slumped marsh sections in marsh sites infested by S. quoianum than in uninfested sites. This effect was also consistent at smaller spatial scales: we found lateral erosion was 300% higher in burrowed areas than in adjacent (within approx. 1 m) unburrowed areas within infested sites. Our results sug- gest that the prodigious burrowing by dense populations of S. quoianum can accelerate erosion rates in saltmarshes and are substantial geomorphic agents of change in estuaries on the Pacific coast of North America.

Nonindigenous species (NIS) that achieve high densities in their recipient communities are expected to have negative effects on native competitors. However, recent reviews have shown that competitors, unlike predators and parasites, have rarely been documented to cause extinctions. There is a need for better understanding of competitive interactions between nonindigenous species and native competitors across systems where NIS reach high densities. In this paper we examine competitive interactions between the exotic, invasive New Zealand mud snail Potamopyrgus antipodarum and native estuarine invertebrates. P. antipodarum is often described as a freshwater snail but can occur in brackish water as well; it has been established in the Columbia River Estuary for over ten years. We addressed competition in this estuarine system using three approaches: field surveys of the benthic invertebrate community, stable isotope analysis of overlap in resource use by common invertebrates, and a laboratory competition experiment that tested the strength of competition between P. antipodarum and the isopod, Gnorimosphaeroma insulare, which overlap in resource use. We found no evidence of negative competitive impacts of P. antipodarum on native benthic invertebrates in this estuarine system. Densities of P. antipodarum and common native epibenthic invertebrates are positively correlated in the intertidal, likely due to shared habitat preferences. The competition experiment showed that the effect of interspecific competition from P. antipodarum on the foraging and survival of G. insulare was significantly less than the effect of intraspecific competition between isopods. The presence of the isopod G. insulare reduced foraging in P. antipodarum, but this change did not result in reduced survival and growth of snails. Hence, interspecific competition is weak despite high densities achieved by the invading species. Finally, we discuss several possible explanations for the observation that P. antipodarum does not have an obvious negative competitive impact on native benthic invertebrates.

The New Zealand mud snail Potamopyrgus antipodarum (Gray, 1843) is a common invasive species in fresh and brackish water ecosystems in Europe, Australia, Japan, and North America. In some invaded habitats, P. antipodarum can reach high densities (over 500,000 snails m -2 ) and dominate the biomass of the benthos, leading to detrimental impacts to native biota and changes in ecosystem dynamics. We report the previously unpublished occurrence of P. antipodarum in thirteen fresh and brackish water systems adjacent to the Pacific coast of North America including a new northern range for P. antipodarum: Port Alberni, Vancouver Island, British Columbia, Canada (49.2479o, -124.8395o). We hypothesize the snail was spread from the Columbia River Estuary to Port Alberni via recreational watercraft or infected fishing equipment. Its discovery in Port Alberni reveals the potential for other aquatic nuisance species in the lower Columbia River to spread to British Columbia. Resource managers on the Pacific coast should remain vigilant and educate the public to prevent the further spread of the P. antipodarum as well as other aquatic invaders.

In the USA, thousands of volunteers are engaged in tracking plant and animal phenology through a variety of citizen science programs for the purpose of amassing spatially and temporally comprehensive datasets useful to scientists and resource managers. The quality of these observations and their suitability for scientific analysis, however, remains largely unevaluated. We aimed to evaluate the accuracy of plant phenology observations collected by citizen scientist volunteers following protocols designed by the USA National Phenology Network (USA-NPN). Phenology observations made by volunteers receiving several hours of formal training were compared to those collected independently by a professional ecologist. Approximately 11,000 observations were recorded by 28 volunteers over the course of one field season. Volunteers consistently identified phenophases correctly (91 % overall) for the 19 species observed. Volunteers demonstrated greatest overall accuracy identifying unfolded leaves, ripe fruits, and open flowers. Transitional accuracy decreased for some species/phenophase combinations (70 % average), and accuracy varied significantly by phenophase and species (p

One of the most obvious impacts roads have on the natural world is direct mortality to individual animals that attempt to cross roads. A less obvious but likely more important impact of roads on many species is habitat fragmentation. The ability for individuals to travel between subpopulations is the key to genetic diversity as well as ultimately the survival of the species. Considering these impacts and management goals to increase habitat connectivity, increased attention has been given to creating road design that reduces wildlife collisions. Most studies, however, have been in other countries or regions and most focus on connectivity for just one or a few species and rarely in urban settings. This study examines the effectiveness of a variety of under-road passage structures for a community of animals in an urban wetland. Wildlife passage was taken into great consideration in the construction of the Boeckman Road Extension, the new road (2006) in Wilsonville, Oregon, examined in this study. As a result it includes a bridge, two box culverts and eleven round concrete culverts to facilitate wildlife passage as well as a mammal fence atop an amphibian/reptile wall. In order to monitor passage use the authors used a combination of sand-track monitoring and motion-detection cameras. They compared passage structure use to movement in the habitats surrounding the road by monitoring four habitat transects in addition to the passage structures (Road transect). They also conducted tag and release studies targeted to small mammals. Finally, camera data collected in passage structures were compared to camera monitoring at the end of the exclusionary fencing. A total of 26 species were detected in this study, 73% (19) of which were found to be using passage structures. 15% (4) of the identified species were detected on transects but not in passages and 11.5% (3) were detected in locations other than transects or passage structures. The bridge structure provided passage to the highest number of species (16), followed by the 24” and 18” culverts, which had a combined total of 11 species, and lastly the 9x4 culverts, which were flooded, with 2 species detected. The results indicate that large and medium mammals overall did not use passages less than would be expected based on their local movement in habitats. In pit and Sherman traps 16 of the 48 small mammals that were captured and tagged were re-caught, but only four of these moved from one transect to another, with two moving away from the road and the other two moving toward and under the road. Of the species detected with cameras at the passage structures and circumventing fencing, excluding small mammals, reptiles and amphibians (139), 19% (33) were found potentially crossing on the road surface. The proportion of deer detected using over-road crossings (23%) is of particular concern for driver safety. The bridge structure provided the greatest passage, in not only frequency of crossings but also species present. When maintenance factors, driver safety and species of greatest concern are included, the higher cost of the bridge structure would likely be even further balanced by the benefits. This study highlights the effectiveness and potential problems (and possible fixes) of some of the passage and prevention structures. Including passage and prevention structures such as these in road design is imperative for habitat connectivity and the need for this becomes even more apparent as Oregon’s native wildlife face an ever increasing urban landscape as well as the potential impacts of climate change.