9 research outputs found
Evaluation of the pilot of domestic violence protection orders
In 2011/12, a 15 month pilot took place in three police force areas (Greater Manchester, West Mercia and Wiltshire) to test a new civil provision, Domestic Violence Protection Orders (DVPOs). DVPOs were designed to provide immediate protection for victim-survivors following a domestic violence incident in circumstances where, in the view of the police, there are no other enforceable restrictions that can be placed upon the perpetrator. DVPOs aim to give victim-survivors time, space and support to consider their options by placing conditions on perpetrators, including restricting/removing perpetrators from households, and preventing contact with, or molestation of, victim-survivors. The approach, introduced by the Crime and Security Act 2010, comprises an initial temporary notice (Domestic Violence Protection Notice, DVPN), authorised by a senior police officer and issued to the perpetrator by the police, followed by a DVPO that can last from 14 to 28 days, imposed at the magistratesâ court
Evaluation of the pilot of domestic violence protection orders
In 2011/12, a 15 month pilot took place in three police force areas (Greater Manchester, West Mercia and Wiltshire) to test a new civil provision, Domestic Violence Protection Orders (DVPOs). DVPOs were designed to provide immediate protection for victim-survivors following a domestic violence incident in circumstances where, in the view of the police, there are no other enforceable restrictions that can be placed upon the perpetrator. DVPOs aim to give victim-survivors time, space and support to consider their options by placing conditions on perpetrators, including restricting/removing perpetrators from households, and preventing contact with, or molestation of, victim-survivors. The approach, introduced by the Crime and Security Act 2010, comprises an initial temporary notice (Domestic Violence Protection Notice, DVPN), authorised by a senior police officer and issued to the perpetrator by the police, followed by a DVPO that can last from 14 to 28 days, imposed at the magistratesâ court
In-group reassurance in a pain setting produces lower levels of physiological arousal: Direct support for a self-categorization analysis of social influence
A large body of research demonstrates a strong social component to people's pain experiences and pain-related behaviours. We investigate this by examining the impact of social-influence processes on laboratory-induced pain responses by manipulating the social-categorical relationship between the person experiencing pain and another who offers reassurance. We show that physiological arousal associated with laboratory-induced pain is significantly lower in normal, healthy participants following reassurance about the pain-inducing activity when that reassurance comes from an ingroup member in contrast to reassurance from an out-group member and a no reassurance control. These data are consistent with predictions derived from self-categorization theory, providing convincing empirical support of its analysis of social influence using a non-reactive measure. These data also represent a clear advance within the pain literature by identifying a possible common process to the social-psychological component of pain responses
Insect pollinators: linking research and policy. Workshop report.
EXECUTIVE SUMMARY
Pollinators interact with plants to underpin wider biodiversity, ecosystem function, ecosystem services to agricultural crops and ultimately human nutrition. The conservation of pollinators is thus an important goal.
Pollinators and pollination represent a tractable example of how biodiversity can be linked to an ecosystem service. This represents a case study for exploring the impacts of various policy instruments aiming to halt/reverse the loss of ecosystem services.
There is a need to understand how multiple pressures (e.g. habitat loss, fragmentation and degradation, climate change, pests and diseases, invasive species and environmental chemicals) can combine or interact to affect diversity, abundance and health of different pollinator groups.
Decision makers need to balance consideration of the effects of single pressures on pollinators against the suite of other pressures on pollinators. For instance, the threat from pesticide use (with its high public and media profile) also needs to be considered in the context of the other threats facing pollinators and balanced against the need for food security. An independent review of the balance of risks across pollinator groups from pesticide use would help synthesise current knowledge into an accessible form for decision makers.
To manage or lessen these threats to pollinators (wild and managed) and pollination requires improved knowledge about their basic ecology. We still need to know where and in what numbers different pollinator species occur, how they use different environments, how they interact with each other through shared plants and diseases and how wild pollinator abundance is changing.
Decision makers need clear factual evidence for i) the relative contribution of different managed and wild pollinator groups to wildflower and crop pollination and ii) how this varies across different land-uses, ecosystems and regions.
Addressing these basic and applied questions will improve our ability to forecast impacts on pollination service delivery to agricultural crops arising from current and future environmental changes, pesticide use and emerging diseases.
The development of a long-term, multi-scale monitoring scheme to monitor trends in pollinator (wild and managed) population size and delivery of pollination services (ideally tied to data collection on land-use, pesticide applications and disease incidence at relevant spatial scales) would provide the evidence base for developing the effectiveness of policy and management interventions over time.
Such a monitoring scheme would benefit from including research council organisations (e.g. CEH), governmental departments (e.g. Fera), universities, museums and NGOs (e.g. BBKA,SBA, Bumblebee Conservation Trust etc)
Insect Pollinators: linking research and policy Workshop Report | 5
In the context of agricultural intensification and conservation we need to establish what type, quality and quantity of interventions (e.g. agri-environment schemes, protected areas) are needed, where to place them and how they can sustain different pollinator populations and effective pollination services.
Current monitoring of the risks from diseases and pesticides requires broadening to consider other insects aside from honey bees, unless we can demonstrate that honey bees are good surrogates for all other pollinators.
There is a need to increase confidence in regulatory risk assessments pertaining to pathogens and pesticides by incorporating other pollinator species, investigating chronic exposure to multiple chemicals and using field relevant dosages (specific to regions, not using other data sources as surrogates).
At present the effects of spatial, social and temporal scales on the benefits stakeholders receive from pollination services are only beginning to be understood.
Economic valuation of pollination services can help optimise the cost-effectiveness of service management measures and offer new opportunities to incentivise action or raise awareness among stakeholders.
Novel tools and instruments (e.g. education and training) are needed to translate broad international (e.g. CBD, EU Biodiversity Strategy) and national (e.g. Englandâs Biodiversity Strategy) policies into local actor (e.g. beekeeper, farmer, citizen scientist) contributions to meet biodiversity commitments
Refocusing some public funding to link basic science to development of practical solutions (e.g. better crop protection products, improved disease resistance or treatment) could help science deliver better-targeted evidence for pollinator protection.
Scientists need to make more use of opportunities (e.g. POSTnotes1; practitioner guides) to transfer knowledge to a broad audience in order to better influence decision maker and practitioner behaviours.
Improved knowledge exchange between scientists and decision makers is important to combating threats to pollination. Central to this is improved understanding of the respective positions of policy makers and scientists. For instance, policy-makers usually need to be presented with a range of options to balance against other areas of policy. Science does not always arrive at a consensus due to uncertainties in data or models. Policy-makers need to understand that scientists are communicating the âbest available knowledge at presentâ and that consequently it is not always possible to give a definitive answer
Annexin A1 expression in a pooled breast cancer series : Association with tumor subtypes and prognosis
Background: Annexin A1 (ANXA1) is a protein related with the carcinogenesis process and metastasis formation in many tumors. However, little is known about the prognostic value of ANXA1 in breast cancer. The purpose of this study is to evaluate the association between ANXA1 expression, BRCA1/2 germline carriership, specific tumor subtypes and survival in breast cancer patients. Methods: Clinical-pathological information and follow-up data were collected from nine breast cancer studies from the Breast Cancer Association Consortium (BCAC) (n = 5,752) and from one study of familial breast cancer patients with BRCA1/