Long Term Implications on Male Children Who Witness Interparental Violence

The immediate effects of family violence on child witnesses are well documented. Even with this information children often do not receive any services particularly if they have not been physically harmed. What is less evident are the long term effects of, family violence on child witnesses. This study gathered data via a questionnaire from 25 males who were attending a domestic violence education program for assaulting their female partner. The questionnaire addressed childhood experiences such as the witnessing of parental violence, conflict resolution methods observed in childhood and discipline methods used in the home. Additionally, the questionnaire asked about current adult partner relationship conflict and discipline methods used with participant children These findings indicated that 88% of the male participants who had been violent in their adult partner relationship had also witnessed and/ or experienced violence in their home as a child

Does host plant influence parasitism and parasitoid species composition in Lygus rugulipennis? A molecular approach

Lygus Hahn plant bugs (Hemiptera: Miridae) are serious pests of a wide variety of economically important crops in North America. European Peristenus digoneutis Loan and P. relictus Ruthe (Hymenoptera: Braconidae) are being considered for release in Canada as part of a classical biological control program for Lygus. The attractiveness of different host plants to European Peristenus has not been addressed, but may be an important consideration prior to parasitoid release. Lygus rugulipennis Poppius nymphs were collected in the Northern Temperate Atlantic (NTA) ecoregion on red clover (Trifolium pratense L.; Fabaceae) and chamomile (Matricaria recutita L.; Asteraceae), and in the Western European Broadleaf Forest (WEBF) ecoregion on red clover and alfalfa (Medicago sativa L.; Fabaceae). Parasitism levels and parasitoid species were determined using a multiplex PCR assay for P. digoneutis, P. relictus, and P. pallipes Curtis. Mean parasitism levels in L. rugulipennis were 45-49% in the NTA ecoregion and 25-32% in the WEBF ecoregion. However, in neither ecoregion were parasitism levels and parasitoid species compositions significantly different in nymphs from different host plant species. Furthermore, multiparasitism was low despite the fact that P. digoneutis and P. relictus share the same host specie

Can grasshoppers spread common bacterial blight in beans?

Non-Peer ReviewedCommon bacterial blight (CBB) is a seed-borne disease of dry bean that is usually spread through rain-splash, particularly when heavy rain or hail damages plants. CBB can cause a reduction in yield and if the seed becomes infected it will become a primary source of inoculum in the next generation. During drought cycles, we often experience heavy grasshopper infestations in Saskatchewan. Not only do grasshoppers reduce crop yield and lay eggs for the following year, but they may also be responsible for spreading disease as they travel through a crop. This could be the result of feeding damage which allows rain to spread disease, or grasshoppers may be carrying the pathogen from plant to plant causing the disease to spread more rapidly through the field. In August 2002, a dry bean breeding nursery at Saskatoon was heavily infected with CBB during the same time frame as a major grasshopper invasion. This research was designed to determine if the grasshoppers themselves can physically spread the disease from plant to plant or if they just damage the plants, making them more susceptible to infection

Do grasshoppers prefer one species of lentil over another?

Non-Peer ReviewedSevere outbreaks of grasshoppers cause yield losses in many economically important crops. Lentil (Lens culinaris) is particularly susceptible to grasshopper damage. The weather patterns of 2001-2002 in most of the lentil production regions of Saskatchewan contributed to the outbreak in grasshopper populations resulting in major damage to the lentil crop. Grasshoppers preferentially target the flowers and young pods of lentil plants. Lentil plants, due to their indeterminate growth habit, will re-grow if moisture is available, leading to development of new pods, resulting in delayed maturity and further grasshopper damage. Pods that are damaged or not consumed entirely may shatter or not fill properly. Grasshoppers are known to have very specific feeding habits and may show a range of preference from one plant species to another based on taste or texture. One of the seven known species of lentil has hairy pods. Grasshopper feeding preferences were examined on five lentil species, including the cultivated lentil. The purpose was to determine if grasshoppers prefer to feed on the cultivated lentil compared to four wild species. If they do, it may be possible in future to breed lentil varieties that are less damaged by grasshoppers by using the wild lentil species in the breeding program

Formulation development and delivery of biopesticides

Non-Peer ReviewedBiopesticide formulation development is integral for end product development and risk reduction associated with commercialization and acceptance by the end user. Development of robust formulations for biopesticides is a key step towards advancing this technology into integrated pest management systems. A granular formulation protocol using extrusion-spheronization-fluidized bed drying for biopesticidal bacteria and fungal hypha and spores is described. Establishing low granule water activity (aw, 0.2-0.3) is a key factor in extending the shelf-life of the product. Starch type and amount provided controlled release attributes to the biopesticide granules. Microencapsulation of bioherbicide, Colletotrichum truncatum 00-003B1 (Ct), conidia and bioinsecticide nucleopolyhedrovirus (NPV), by complex coacervation is described for foliar application of biocontrol agents

Ecological consequences of human niche construction: Examining long-term anthropogenic shaping of global species distributions

The exhibition of increasingly intensive and complex niche construction behaviors through time is a key feature of human evolution, culminating in the advanced capacity for ecosystem engineering exhibited by Homo sapiens. A crucial outcome of such behaviors has been the dramatic reshaping of the global biosphere, a transformation whose early origins are increasingly apparent from cumulative archaeological and paleoecological datasets. Such data suggest that, by the Late Pleistocene, humans had begun to engage in activities that have led to alterations in the distributions of a vast array of species across most, if not all, taxonomic groups. Changes to biodiversity have included extinctions, extirpations, and shifts in species composition, diversity, and community structure. We outline key examples of these changes, highlighting findings from the study of new datasets, like ancient DNA (aDNA), stable isotopes, and microfossils, as well as the application of new statistical and computational methods to datasets that have accumulated significantly in recent decades. We focus on four major phases that witnessed broad anthropogenic alterations to biodiversity—the Late Pleistocene global human expansion, the Neolithic spread of agriculture, the era of island colonization, and the emergence of early urbanized societies and commercial networks. Archaeological evidence documents millennia of anthropogenic transformations that have created novel ecosystems around the world. This record has implications for ecological and evolutionary research, conservation strategies, and the maintenance of ecosystem services, pointing to a significant need for broader cross-disciplinary engagement between archaeology and the biological and environmental sciences

Can statin preventative treatment inform geroscience-guided therapeutics?

: Potential senotherapeutic effect of statins may lead to prevention and reduction of frailty

Kelp Forest Ecosystems: Biodiversity, Stability, Resilience and Future

Kelp forests are phyletically diverse, structurally complex and highly productive components of cold-water rocky marine coastlines. This paper reviews the conditions in which kelp forests develop globally and where, why and at what rate they become deforested. The ecology and long archaeological history of kelp forests are examined through case studies from southern California, the Aleutian Islands and the western North Atlantic, well-studied locations that represent the widest possible range in kelp forest biodiversity. Global distribution of kelp forests is physiologically constrained by light at high latitudes and by nutrients, warm temperatures and other macrophytes at low latitudes. Within mid-latitude belts (roughly 40-60degrees latitude in both hemispheres) well-developed kelp forests are most threatened by herbivory, usually from sea urchins. Overfishing and extirpation of highly valued vertebrate apex predators often triggered herbivore population increases, leading to widespread kelp deforestation. Such deforestations have the most profound and lasting impacts on species-depauperate systems, such as those in Alaska and the western North Atlantic. Globally urchin-induced deforestation has been increasing over the past 2-3 decades. Continued fishing down of coastal food webs has resulted in shifting harvesting targets from apex predators to their invertebrate prey, including kelp-grazing herbivores. The recent global expansion of sea urchin harvesting has led to the widespread extirpation of this herbivore, and kelp forests have returned in some locations but, for the first time, these forests are devoid of vertebrate apex predators. In the western North Atlantic, large predatory crabs have recently filled this void and they have become the new apex predator in this system. Similar shifts from fish- to crab-dominance may have occurred in coastal zones of the United Kingdom and Japan, where large predatory finfish were extirpated long ago. Three North American case studies of kelp forests were examined to determine their long history with humans and project the status of future kelp forests to the year 2025. Fishing impacts on kelp forest systems have been both profound and much longer in duration than previously thought. Archaeological data suggest that coastal peoples exploited kelp forest organisms for thousands of years, occasionally resulting in localized losses of apex predators, outbreaks of sea urchin populations and probably small-scale deforestation. Over the past two centuries, commercial exploitation for export led to the extirpation of sea urchin predators, such as the sea otter in the North Pacific and predatory fishes like the cod in the North Atlantic. The largescale removal of predators for export markets increased sea urchin abundances and promoted the decline of kelp forests over vast areas. Despite southern California having one of the longest known associations with coastal kelp forests, widespread deforestation is rare. It is possible that functional redundancies among predators and herbivores make this most diverse system most stable. Such biodiverse kelp forests may also resist invasion from non-native species. In the species-depauperate western North Atlantic, introduced algal competitors carpet the benthos and threaten future kelp dominance. There, other non-native herbivores and predators have become established and dominant components of this system. Climate changes have had measurable impacts on kelp forest ecosystems and efforts to control the emission of greenhouse gasses should be a global priority. However, overfishing appears to be the greatest manageable threat to kelp forest ecosystems over the 2025 time horizon. Management should focus on minimizing fishing impacts and restoring populations of functionally important species in these systems