Academic literature on the topic 'Hazardous substances – Government policy – International cooperation'

Modern directions of activities are reported in the frame of international agreements in chemical safety-The Basel Convention on the control of transboundary movements of hazardous wastes and their disposal, the Rotterdam Convention on the prior informed consent procedure for certain hazardous chemicals and pesticides in international trade, the Stockholm convention on persistent organic pollutants. Taking into account that at the national level, especially in small-size countries, the same bodies represent their countries in international conventions, in 2011 under UNEP, a BRS convention (unified secretariat) was set up to improve coordination of Conventions, to raise the level of their cooperation and at the same time to lower expenses of their activities by setting up common services such as administration support, joimt clearing house, planning and holding meetings of all levels, training, providing technical assistance etc. The three conventions deal with a great number of the same substances in accordance with their objectives and area of activities which requires a deep coordination in the frame of Conventions both at the international and national levels. All three Conventions preserve their full independence but conducting a policy of synenergy that means collaboration and deep coordination,

ABSTRACT As knowledge, policies and infrastructure related to marine oil spill prevention, preparedness and response have continued to evolve and are now considered to have reached a state of relative maturity; attention has more recently turned to developing systems to address spills of hazardous and noxious substances (HNS) in the marine environment. The International Maritime Organization (IMO), as the specialized agency of the United Nations with a global mandate for the protection of the marine environment from pollution caused by shipping, discharges its commitment to protecting the marine environment from pollution from oil and HNS at the global level along four different but interdependent paths: prevention, preparedness and response, and technical co-operation. Two mutually supporting IMO instruments that together address the Prevention-Preparedness-Response (PPR) continuum for HNS are: The International Convention for the Prevention of pollution from Ships, 1973, as modified by the Protocols of 1978 and 1997 relating thereto (MARPOL Convention), notably Annexes II (noxious liquid substances in bulk) and III (harmful substances carried by sea in packaged form), covering prevention, and the Protocol on Preparedness, Response and Co-operation to Pollution Incidents by Hazardous and Noxious Substances, 2000 (HNS Protocol), which addresses preparedness, response and cooperation to spills of HNS. Together, these instruments provide a framework for countries to establish the necessary systems for tackling the complex issue of prevention, preparedness and response to HNS, with the goal of embedding the principles set out in these instruments into national legislation and policy that are fully implemented at both institutional and operational levels. At the same time, it is equally recognized that the topic of preparedness and response to HNS is still in its infancy and that any systems developed must borrow heavily from the established systems for oil pollution, in order to maximize the use of existing capacity in planning and preparing for HNS, at the same time acknowledging the unique issues presented by these substances. The paper will examine these elements in greater detail and will discuss the requirements for developing systems for preparedness and response for oil and HNS, comparing areas of similarity, contrasting the differences and identifying the distinct considerations that are necessary for each.

ABSTRACT This paper focuses on industry and government roles for addressing historic properties during oil spill response. In 1997, the National Response Team (NRT) developed a Programmatic Agreement on Protection of Historic Properties during Emergency Response under the National Oil and Hazardous Substances Pollution Contingency Plan (PA) (National Response Team, 1997). At the 1999 International Oil Spill Conference (IOSC), U.S. Department of the Interior (DOI) representatives discussed the development and implementation of the PA, which is intended to ensure that historic properties are appropriately taken into account during the planning for and conducting of emergency response to oil spills and hazardous substance releases. Following the 1999 IOSC, DOI and Chevron representatives began a dialog regarding industry and government roles under the PA. Chevron invited the DOI representatives to participate in an October 1999 large-scale, industry-led spill exercise; a precedent-setting drill that included historic properties protection as a key objective. This 2001 paper focuses on how industry and government have worked together to protect historic properties, government roles in PA implementation, and lessons learned. As an example of what industry can do to support the protection of historic properties during planning and response activities, this paper describes Chevron's Historic Properties Program, a program managed under its emergency spill response environmental functional team (EFT). A discussion of lessons learned focuses on the need for clear definition of industry and government roles, and the benefits of building a foundation of cooperation between industry and government to protect historic properties. Of particular importance is the inclusion of historic properties in all aspects of oil spill preparedness and response, including planning, drills, training, and response organization structure and staffing. Experience from incident response in Alaska has shown that the PA assists Federal On-Scene Coordinators (FOSCs) and responsible parties, while also protecting historic properties, when the FOSC is prepared to implement the PA promptly and effectively.

Abstract While each region of the world faces unique challenges, environmental threats to vulnerable populations throughout Central and Eastern Europe (CEE) present a significant public health challenge. Environmental pollution is widespread, resulting from the consequences of rapid industrialization during the Soviet Union era. To help address these concerns, a meeting, sponsored in part by the National Institutes of Health (NIH)/National Institute of Environmental Health Sciences (NIEHS) Superfund Research Program (SRP), was convened in 1994. The meeting, “Hazardous Wastes – Exposure, Remediation, and Policy,” brought together representatives of the governments of seven countries in the region, scientists from the United States and Western Europe, and representatives from international organizations to explore hazardous waste problems in the region. Since 1994, the SRP and partners have been holding meetings throughout CEE to share important information regarding environmental health. The general sessions have shifted from a focus on describing the problems in each country related to hazardous waste, exposure assessment, risk reduction, and risk communication, to an exchange of information to better define links between health and the environment and strategies to improve regional problems. The 1994 meeting and subsequent meetings raised issues such as heavy metal contamination, exposures from hazardous waste, and pollution caused by deficiencies in disposal of waste overall. Research priorities that were identified included development of reliable biomarkers, better understanding of the relationship between nutrition and chemical toxicity, more epidemiological studies in CEE, better methods of environmental data analysis, and development of remediation tools. Here, we review examples of research from current SRP grantees that address many of these issues. In 2004, the first official Central and Eastern European Conference on Health and the Environment (CEECHE) was held, and has been held biannually at venues across CEE. The CEECHE provides a forum for researchers and engineers, and organizations with diverse professional expertise and backgrounds, to jointly examine pressing environment and health issues, engage in cooperative research, and develop and disseminate innovative prevention strategies for addressing these issues. The CEECHE facilitates more intentional integration of disciplines to achieve a fundamental understanding of biological, environmental, and engineering processes and exploit this knowledge to contribute to solving environmental exposure-related issues. Critical to the CEECHE mission is the participation of trainees and junior scientists who will share their data and engage broadly with the scientific community. Scientific inquiry that supports a paradigm whereby knowledge gained through understanding disease processes resulting from environmental exposures would further our understanding of potential human health effects, and provide a creative, holistic approach to integrate seemingly discrete biological systems and geological, ecological and human health risk assessments into more comprehensive models. Such models will be discussed which advance the mission of reducing the public health burden of hazardous substances through interdisciplinary research and training.

Recent trends in the organization of work have increased the risk of occupational safety and health (OSH) in Kenyan industries through exposure to hazardous substances, work related accidents and increased stress-related illnesses. According to International lab our organization (ILO) everyone is entitled to the right to safe and healthy working conditions and therefore the corpus of law in Kenya dealing with occupational safety and health should be embedded in the international OSH legal instruments. Specifically the occupational health and safety Act (2007) is expected to provide for safety, health and welfare of workers and all persons lawfully present at workplaces. The purpose of this study therefore was to investigate legal framework as a determinant of implementation of occupational health and safety programmes in the manufacturing sector in Kenya. It focused on six legal areas predicted as affecting implementation of OSH. These factors were national OSH policy, OSHA (occupational safety and health Act) familiarity with OSHA, government OSH inspections and audits, ease of implementation of OSHA, Government support in the implementation of OSH and OSHA implement ability. The study adopted descriptive cross-sectional survey design but however intended to gather both qualitative and quantitative data. A self administered questionnaire was used to collect data from 257 OSH officers drawn randomly from 735 manufacturing industries registered by Kenya manufacturers association. 252 questionnaires were received back and analyzed with the help of SSPS window version 21. Both correlation and regression analysis were conducted and the results showed that there was a positive significant relationship between legal framework and implementation of OSH programmes.

ABSTRACT Participants in the 1991 Oil Spill Conference were informed of the outcome of the IMO Conference on International Cooperation on Oil Pollution Preparedness and Response, in particular the adoption of the International Convention on Oil Pollution Preparedness, Response and Co-operation, 1990 (OPRC). Although 27 States signed it, the OPRC stipulates that it will enter into force or become binding one year after 15 States have accepted or ratified it. Although the OPRC, therefore, is not yet in force, IMO Member States, the Secretary-General of IMO, Mr. William O'Neil, and IMO's Marine Environment Protection Committee (MEPC) have taken concrete actions to facilitate early implementation. In November 1991 the Secretary-General established a coordination center in the Marine Environment Division of IMO to carry out functions assigned to IMO under the OPRC (information services, education and training, technical services, and technical assistance). In March 1992 the MEPC established an OPRC Working Group, in which government and industry experts and representatives of environmental organizations participate, to deal with matters related to implementation of the OPRC. Among the important topics which will be included in the program of the OPRC Working Group through 1992–1993 are links between MARPOL Regulation 26 and OPRC articles 3 and 6 and development of guidelines for the preparation of oil pollution emergency plans for offshore units and seaports; update of IMO's Manual on Oil Pollution, Section II—Contingency Planning; development of guidelines or recommendations on facilitating the movement of response equipment and personnel and the use of response resources during marine pollution incidents; development of research and development clearinghouse functions; development of model training courses and an OPRC training plan; and consideration of ways to expand the scope of the OPRC to include hazardous and noxious substances.

Environmental crime is one of the most lucrative forms of criminal activity. The illegal dumping of hazardous waste, trafficking of dangerous substances and smuggling of protected natural resources is estimated to be worth between EUR18 and EUR25 billion per year. The trafficking of endangered species generates the highest revenue of all types of environmental crime and is widely considered to be second in value only to drug trafficking. Environmental crime is believed to be expanding constantly. In spite of this, it is not currently a political priority, having taken a back seat to anti-terrorism measures since 11 September 2001. This article aims to show that environmental crime is one of the most serious forms of criminal activity - it threatens the very existence of mankind. In order to do this, the article begins by advancing a definition of environmental crime, which is intended to allow the reader better to understand its implications for our society. An attempt is then made to provide a financial estimate of the worldwide value of this criminal activity, in order to shed light on its scale and diversity. Next, the article examines various examples from European Union (?EU?) countries (Member States and candidate countries) in order to illustrate the ways in which police combat environmental crime. Examples of international cooperation in this field are also provided. Finally, the article proposes a number of possible paths for future action which might push environmental crime up the criminal law and crime-fighting policy agenda in EU Member States and EU policy as a whole. In this respect, the recent judgment by the European Court of Justice (?ECJ?) concerning European Community competence in criminal law provides interesting material for reflection.

The article presents the scientific results which are a generalization of almost twenty years of experience of the staff of the department of information technology and security systems of the Russian State Hydrometeorological University in the field of remote sensing methods of oil pollution on the water surface. The choice of radar systems for the implementation of remote monitoring of the water surface on the characteristics of efficiency and coverage of the area of responsibility is substantiated. Structurally, the radar monitoring system should consist of a network of centimeter and millimeter range radar systems. The use of centimeter-range radar systems is due to the preservation of their operability during intense precipitation. Millimeter-wave radar systems are characterized by higher radar contrast, which significantly increases the effectiveness of environmental monitoring of water areas, their performance depending on the weather conditions. Thus, a combination of radars of two ranges allows continuous monitoring of the water area in any weather conditions. Radar systems are a recording module as part of an object monitoring system. The facility monitoring system, in addition to existing systems at the regional level, allows to receive information on the environmental situation promptly. This is especially true in case of emergency situations that occur during loading and transportation of oil products and other environmentally hazardous substances. The most significant result of many years of research is the concept of an automated distributed system for remote environmental monitoring of the water surface. For each module of the system, methods and models for processing spatial data and algorithms for the distribution of measuring instruments in the monitoring space are proposed. The purpose of the functioning of such a system is associated with detecting oil spills on the water surface, monitoring the dynamics of pollution and predicting the development of emergencies resulting from environmental disasters. International cooperation in the field of environmental protection is shown to be international in nature, the joint projects being an effective tool for development of scientific and educational potential of higher education in the field of ecology. Participation in international projects not only allows to increase the scientific and educational potential of higher education, but also influences the formation of environmental policy

In this era of startling developments in the medical field there remains a serious worry about the hazardous potential of various by products which if not properly addressed can lead to consequences of immense public concern. Hospitals and other health care facilities generate waste products which are evidently hazardous to all those exposed to its potentially harmful effects. Need for effective legislation ensuring its safe disposal is supposed to be an integral part of any country's health related policy. This issue is of special importance in developing countries like Pakistan which in spite of framing various regulations for safeguarding public health, seem to overlook its actual implementation. The result unfortunately is the price wehave to pay not only in terms of rampant spread of crippling infections but a significant spending of health budget on combating epidemics which could easily have been avoided through effective waste disposal measures in the first place. Waste classified under the heading 'bio-hazardous' includes any infectious or potentially infectious material which can be injurious or harmful to humans and other living organisms. Amongst the many potential sources are the hospitals or other health delivery centres which are ironically supposed to be the centres of infection control and treatment. Whilst working in these setups, health care workers such as doctors, nurses, paramedical staff and sanitation workers are actually the ones most exposed and vulnerable to these challenges. Biomedical waste may broadly be classified into Infectious and toxic waste. Infectious waste includes sharps, blood, body fluids and tissues etcwhile substances such as radioactive material and by-products of certain drugs qualify as toxic waste. Furthermore health institutions also have to cater for general municipal waste such as carton boxes, paper and plastics. The World Health Organisation has its own general classification of hospital waste divided into almost eight categories of which almost 15% (10% infectious and 5% toxic) is estimated to be of a hazardous nature while the remaining 85% is general non hazardous content.1A recent study from Faisalabad, Pakistan has estimated hospital waste generation around 1 to 1.5 kg / bed /day for public sector hospitals in the region,2while figures quoted from neighbouring India are approximately 0.5 to 2 KG / hospital bed /day.3 Elsewhere in the world variable daily hospital waste production has been observed ranging from as low as 0.14 to 0.49 kg /day in Korea4 and 0.26 to 0.89 kg/day in Greece5to as high as 2.1 to 3.83 kg/day in Turkey6 and 0.84 to 5.8 kg/day in Tanzania.7Ill effects of improper management of hospital waste can manifest as nosocomial infections or occupational hazards such as needle stick injuries. Pathogens or spores can be borne either through the oro-faecal or respiratory routes in addition to direct inoculation through contact with infected needles or sharps. Environmental pollution can result from improper burning of toxic material leading to emission of dioxins, particulate matter or furans into the air. The habitat can also be affected by illegal dumping and landfills or washing up of medical waste released into the sea or river. Potential organisms implicated in diseases secondary to mismanagement of hospital waste disposal include salmonella, cholera, shigella, helminths, strep pneumonia, measles, tuberculosis, herpesvirus, anthrax, meningitis, HIV, hepatitis and candida etc. These infections can cause a considerable strain on the overall health and finances of the community or individuals affected. The basic principal of Public health management i.e 'prevention is better than cure' cannot be more stressed in this scenario as compared to any other health challenge. Health facilities must have a clear policy on hazardous waste management. To ensure a safe environment hospitals need to adopt and implement international and local systems of waste disposal. Hospital waste management plan entails policy and procedures addressing waste generation, accumulation, handling, transportation, storage, treatment and disposal. Waste needs to be collected in marked containers usually colour coded and leak proof. Segregation at source is of vital importance. The standard practice in many countries is the Basic Three Bin System ie to segregate the waste into RED bags/ boxes for sharps, YELLOW bags for biological waste and BLUE or BLACK ones for general/ municipal waste. All hospital staff needs to be trained in the concept of putting the right waste in relevant containers/ bags. They need to know that more than anything else this practice is vital for their own safety. The message can be reinforced through appropriate labelling on the bins and having posters with simple delineations to avoid mixing of different waste types. Sharps essentially should be kept in rigid, leak and puncture-resistant containers which are tightly lidded and labelled. Regular training sessions for nurses and cleaning staff can be organised as they are the personnel who are more likely to deal with waste disposition at the level of their respective departments. Next of course is transportation of waste products to the storage or disposal. Sanitary staff and janitors must be aware of the basic concepts of waste handling and should wear protective clothing, masks and gloves etc, besides ensuring regular practice of disinfection and sterilization techniques.8Special trolleys or vehicles exclusively designed and reserved for biomedical waste and operated by trained individuals should be used for transportation to the dumping or treatment site. Biomedical waste treatment whether on site or off site is a specialised entity involving use of chemicals and equipment intended for curtailing the hazardous potential of the material at hand. Thermal treatment via incinerators, not only results in combustion of organic substances but the final product in the form of non-toxicash is only 10 to 15% of the original solid mass of waste material fed to the machine. Dedicated autoclaves and microwaves can also be used for the purpose of disinfection. Chemicals such as bleach, sodium hydroxides, chlorine dioxide and sodiumhypochlorite are also effective disinfectants having specialised indications. Countries around the world have their own regulations for waste management. United Kingdom practices strict observance of Environmental protection act 1990, Waste managementlicensing regulations 1994 and Hazardous waste regulations 2005 making it one of thesafest countries in terms of hazardous waste disposal. Similar regulations specific for each state have been adopted in United States following passage of the Medical Waste tracking act 1988. In Pakistan, every hospital must comply with the Waste Management Rules 2005 (Environment Protection Act 1997), though actual compliance is far from satisfactory. It is high time that the government and responsible community organisations shape up to seriously tackle the issue of bio hazardous waste management through enforcement of effective policies and standard operating procedures for safeguarding the health and lives of the public in general and health workers in particular.

In this era of startling developments in the medical field there remains a serious worry about the hazardous potential of various by products which if not properly addressed can lead to consequences of immense public concern. Hospitals and other health care facilities generate waste products which are evidently hazardous to all those exposed to its potentially harmful effects. Need for effective legislation ensuring its safe disposal is supposed to be an integral part of any country's health related policy. This issue is of special importance in developing countries like Pakistan which in spite of framing various regulations for safeguarding public health, seem to overlook its actual implementation. The result unfortunately is the price wehave to pay not only in terms of rampant spread of crippling infections but a significant spending of health budget on combating epidemics which could easily have been avoided through effective waste disposal measures in the first place. Waste classified under the heading 'bio-hazardous' includes any infectious or potentially infectious material which can be injurious or harmful to humans and other living organisms. Amongst the many potential sources are the hospitals or other health delivery centres which are ironically supposed to be the centres of infection control and treatment. Whilst working in these setups, health care workers such as doctors, nurses, paramedical staff and sanitation workers are actually the ones most exposed and vulnerable to these challenges. Biomedical waste may broadly be classified into Infectious and toxic waste. Infectious waste includes sharps, blood, body fluids and tissues etcwhile substances such as radioactive material and by-products of certain drugs qualify as toxic waste. Furthermore health institutions also have to cater for general municipal waste such as carton boxes, paper and plastics. The World Health Organisation has its own general classification of hospital waste divided into almost eight categories of which almost 15% (10% infectious and 5% toxic) is estimated to be of a hazardous nature while the remaining 85% is general non hazardous content.1A recent study from Faisalabad, Pakistan has estimated hospital waste generation around 1 to 1.5 kg / bed /day for public sector hospitals in the region,2while figures quoted from neighbouring India are approximately 0.5 to 2 KG / hospital bed /day.3 Elsewhere in the world variable daily hospital waste production has been observed ranging from as low as 0.14 to 0.49 kg /day in Korea4 and 0.26 to 0.89 kg/day in Greece5to as high as 2.1 to 3.83 kg/day in Turkey6 and 0.84 to 5.8 kg/day in Tanzania.7Ill effects of improper management of hospital waste can manifest as nosocomial infections or occupational hazards such as needle stick injuries. Pathogens or spores can be borne either through the oro-faecal or respiratory routes in addition to direct inoculation through contact with infected needles or sharps. Environmental pollution can result from improper burning of toxic material leading to emission of dioxins, particulate matter or furans into the air. The habitat can also be affected by illegal dumping and landfills or washing up of medical waste released into the sea or river. Potential organisms implicated in diseases secondary to mismanagement of hospital waste disposal include salmonella, cholera, shigella, helminths, strep pneumonia, measles, tuberculosis, herpesvirus, anthrax, meningitis, HIV, hepatitis and candida etc. These infections can cause a considerable strain on the overall health and finances of the community or individuals affected. The basic principal of Public health management i.e 'prevention is better than cure' cannot be more stressed in this scenario as compared to any other health challenge. Health facilities must have a clear policy on hazardous waste management. To ensure a safe environment hospitals need to adopt and implement international and local systems of waste disposal. Hospital waste management plan entails policy and procedures addressing waste generation, accumulation, handling, transportation, storage, treatment and disposal. Waste needs to be collected in marked containers usually colour coded and leak proof. Segregation at source is of vital importance. The standard practice in many countries is the Basic Three Bin System ie to segregate the waste into RED bags/ boxes for sharps, YELLOW bags for biological waste and BLUE or BLACK ones for general/ municipal waste. All hospital staff needs to be trained in the concept of putting the right waste in relevant containers/ bags. They need to know that more than anything else this practice is vital for their own safety. The message can be reinforced through appropriate labelling on the bins and having posters with simple delineations to avoid mixing of different waste types. Sharps essentially should be kept in rigid, leak and puncture-resistant containers which are tightly lidded and labelled. Regular training sessions for nurses and cleaning staff can be organised as they are the personnel who are more likely to deal with waste disposition at the level of their respective departments. Next of course is transportation of waste products to the storage or disposal. Sanitary staff and janitors must be aware of the basic concepts of waste handling and should wear protective clothing, masks and gloves etc, besides ensuring regular practice of disinfection and sterilization techniques.8Special trolleys or vehicles exclusively designed and reserved for biomedical waste and operated by trained individuals should be used for transportation to the dumping or treatment site. Biomedical waste treatment whether on site or off site is a specialised entity involving use of chemicals and equipment intended for curtailing the hazardous potential of the material at hand. Thermal treatment via incinerators, not only results in combustion of organic substances but the final product in the form of non-toxicash is only 10 to 15% of the original solid mass of waste material fed to the machine. Dedicated autoclaves and microwaves can also be used for the purpose of disinfection. Chemicals such as bleach, sodium hydroxides, chlorine dioxide and sodiumhypochlorite are also effective disinfectants having specialised indications. Countries around the world have their own regulations for waste management. United Kingdom practices strict observance of Environmental protection act 1990, Waste managementlicensing regulations 1994 and Hazardous waste regulations 2005 making it one of thesafest countries in terms of hazardous waste disposal. Similar regulations specific for each state have been adopted in United States following passage of the Medical Waste tracking act 1988. In Pakistan, every hospital must comply with the Waste Management Rules 2005 (Environment Protection Act 1997), though actual compliance is far from satisfactory. It is high time that the government and responsible community organisations shape up to seriously tackle the issue of bio hazardous waste management through enforcement of effective policies and standard operating procedures for safeguarding the health and lives of the public in general and health workers in particular. Outbreaks, defined as excess cases of a particular disease or illness which outweighs the response capabilities, have the capacity to overwhelm health care facilities and need timely response and attention to details in order to avoid potentially disastrous sequelae . In this day and age when improvement in public health practices have significantly curtailed outbreak of various diseases, certain viral illnesses continue to make headlines. One of the notable vector borne infectious disease affecting significant portions of south east Asia in the early part of twenty first century is 'Dengue fever'. Dreaded as it is by those suffering from the illness, a lot of the hysteria created is secondary to a lack of education and understanding of the nature of the disease and at times a result of disinformation campaign for vested interests by certain political and media sections.'Dengue' in fact is a Spanish word, assumed to have originated from the Swahili phrase -ka dinga peppo -which describes the disease as being caused by evil spirit. 1 Over the course of time it has been called 'breakbone fever', 'bilious vomiting fever', 'break heart fever', 'dandy fever', 'la dengue' and 'Phillipine, Thai and Singapore hemorrhagic fever' Whilst the first reported case referring to dengue fever as a water poison spread by flying insects, exists in the Chinese medical encyclopedia from Jin Dynasty (265-420 AD), the disease is believed to have disseminated from Africa with the spread of the primary vector, aedes egypti, in the 15th to 19th century as a result of globalisation of slave trade 45In 80% of the patients affected by this condition the presentation is rather insidious and at best characterized by mild fever. The classical 'Dengue fever' present in about 5% of the cases is characterized by high temperature, body aches, vomiting and at times a skin rash. The disease may regresses in two to seven days. However inrare instances (<5%) it may develop into more serious conditions such as Dengue hemorrhagic fever whereby the platelet count is significantly reduced leading to bleeding tendencies and may even culminate in a more life threatening presentation i.e Dengue shock syndrome.6To understand the actual dynamics of Dengue epidemic it is important to understand the mode of its spread in affected areas. Aedes mosquito (significantly Aedes Egypti) acts a vector for this disease. Early morning and evening times7 are favoured by these mosquitos to feed on their prey. There is some evidence that the disease may be transmitted via blood products and organ donation. 8 Moreover vertical transmission (mother to child) has also been reported 9Diagnostic investigations include blood antigen detection through NS-I or nucleic acid detection via PCR. IO Cell cultures and specific serology may also be used for confirming the underlying disease. Whilst sporadic and endemic cases are part of routine medical practice and may not raise any alarm bells, outbreaks certainly need mobilization of appropriate resources for effective control. Needless to say 'prevention is better than cure' and should be the primary target of the health authorities in devising strategies for disease control.The WHO recommended 'Integrated Vector control programme', lays stress on social mobilisation and strengthening of public health bodies, coherent response of health and related departments and effective capacity building of relevant personnel and organisations as well as the community at risk. For Aedes Egypti the primary control revolves around eliminating its habitats such as open sources of water. In a local perspective in our city Peshawar, venue of the recent dengue epidemic, it may be seen in the form of incidental reservoirs such as receptacles and tyres dumped in open areas such as roof tops with rain water accumulating in them and provtdjng excellent breeding habitats, Larvicidal and insecticides may be added to more permanent sources such as watertanks and farm lands. There is not much of a role for spraying with organophosphorous agents which is at times resorted to for public consumption. Public education is the key to any effective strategy which must highlight the need for wearing clothing that fully covers the skin, avoiding unnecessary early morning and evening exposure to vector agents, application of insect repellents and use of mosquito nets. It is also important not to panic if affliction with the disease is suspected as in a vast majority of instances it is a self limiting illness without any long term harmful effects and needs simple conservative management like antipyretics and analgesics.An important consideration for responsible authorities in a dengue epidemic is to ensure that maximum management facilities for simple cases are provided at the community level through primary and secondary health care facilities and that the tertiary care hospitals are not inundated with all sort of patients demanding consultation. These later facilities should be reserved for those patients who end up with any complications or more severe manifestation of the disease.Research is underway to develop an ideal vaccine for Dengue fever. In 2016, a vaccine by the name 'Dengvaxia' was marketed in Phillipines and Indonesia. However with development of new serotypes of the virus, its efficacy has been somewhat compromised.As for treatment , there are no specific antiviral drugs. Management is symptomatic revolving mainly around oral and intravenous hydration. Paracetamol (Acetaminophen) is used for fever as compared to NSAIDS such as Ibuprophen infusion as well as blood and platelet transfusion.Data to date shows that slightly more than twenty three thousand people have been diagnosed with dengue over the past three months ie August to October there is a lower risk of bleeding with the former. Those with more severe form of the disease may need Dextran 2017, in Peshawar, Pakistan with around fourteen thousand needing admission and about sixty nine recorded deaths. The mortality is well within the acceptable international standards of less than 1% for the disease. In the backdrop of all the debate surrounding the current epidemic, one can infer that such outbreaks are best addressed with effective planningwell ahead of the time before the disease threatens to spiral out of control. Simple measures such as covering water storage facilities, using larvicidals where practical, use of insect repellents, mosquito nets and avoiding unnecessary exposure can offerthe best protection. Public health messages via print and electronic media can help educate people in affected areas and allay any anxiety building up from a fear of developing life threatening complications. Health department must mobilise all its resources to ensure local management of diagnosed patients with simple dengue fever and facilitate hospital admission only for those suffering from more severe form of the disease. Moreover the media hype into such situations needs to be addressed through constant updates and discouraging any negative politicking on the issue. To sum up Dengue fever is not really an affliction to be dreaded provided it is viewed and managed in the right perspective.