From Fog to Smog: the Value of Pollution Information∗
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Soil Contamination and Human Health: a Major Challenge For
Soil contamination and human health : A major challenge for global soil security Florence Carre, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, Martine Ramel To cite this version: Florence Carre, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, et al.. Soil con- tamination and human health : A major challenge for global soil security. Global Soil Security Sympo- sium, May 2015, College Station, United States. pp.275-295, 10.1007/978-3-319-43394-3_25. ineris- 01864711 HAL Id: ineris-01864711 https://hal-ineris.archives-ouvertes.fr/ineris-01864711 Submitted on 30 Aug 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Human Health as another major challenge of Global Soil Security Florence Carré, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, Martine Ramel Abstract This chapter aimed to demonstrate, by several illustrated examples, that Human Health should be considered as another major challenge of global soil security by emphasizing the fact that (a) soil contamination is a worldwide issue, estimations can be done based on local contamination but the extent and content of diffuse contamination is largely unknown; (b) although soil is able to store, filter and reduce contamination, it can also transform and make accessible soil contaminants and their metabolites, contributing then to human health impacts. -
What's in the Air Gets Around Poster
Air pollution comes AIR AWARENESS: from many sources, Our air contains What's both natural & manmade. a combination of different gasses: OZONE (GOOD) 78% nitrogen, 21% oxygen, in the is a gas that occurs forest fires, vehicle exhaust, naturally in the upper plus 1% from carbon dioxide, volcanic emissions smokestack emissions atmosphere. It filters water vapor, and other gasses. the sun's ultraviolet rays and protects AIRgets life on the planet from the Air moves around burning Around! when the wind blows. rays. Forests can be harmed when nutrients are drained out of the soil by acid rain, and trees can't Air grow properly. pollution ACID RAIN Water The from one place can forms when sulfur cause problems oxides and nitrogen oxides falls from 1 air is in mix with water vapor in the air. constant motion many miles from clouds that form where it Because wind moves the air, acid in the air. Pollutants around the earth (wind). started. rain can fall hundreds of miles from its AIR MONITORING: and tiny bits of soil are As it moves, it absorbs source. Acid rain can make lakes so acidic Scientists check the quality of carried with it to the water from lakes, rivers that plants and animals can't live in the water. our air every day and grade it using the Air Quality Index (AQI). ground below. and oceans, picks up soil We can check the daily AQI on the from the land, and moves Internet or from local 2 pollutants in the air. news sources. Greenhouse gases, sulfur oxides and Earth's nitrogen oxides are added to the air when coal, oil and natural gas are CARS, TRUCKS burned to provide Air energy. -
Wildland Fire Incident Management Field Guide
A publication of the National Wildfire Coordinating Group Wildland Fire Incident Management Field Guide PMS 210 April 2013 Wildland Fire Incident Management Field Guide April 2013 PMS 210 Sponsored for NWCG publication by the NWCG Operations and Workforce Development Committee. Comments regarding the content of this product should be directed to the Operations and Workforce Development Committee, contact and other information about this committee is located on the NWCG Web site at http://www.nwcg.gov. Questions and comments may also be emailed to [email protected]. This product is available electronically from the NWCG Web site at http://www.nwcg.gov. Previous editions: this product replaces PMS 410-1, Fireline Handbook, NWCG Handbook 3, March 2004. The National Wildfire Coordinating Group (NWCG) has approved the contents of this product for the guidance of its member agencies and is not responsible for the interpretation or use of this information by anyone else. NWCG’s intent is to specifically identify all copyrighted content used in NWCG products. All other NWCG information is in the public domain. Use of public domain information, including copying, is permitted. Use of NWCG information within another document is permitted, if NWCG information is accurately credited to the NWCG. The NWCG logo may not be used except on NWCG-authorized information. “National Wildfire Coordinating Group,” “NWCG,” and the NWCG logo are trademarks of the National Wildfire Coordinating Group. The use of trade, firm, or corporation names or trademarks in this product is for the information and convenience of the reader and does not constitute an endorsement by the National Wildfire Coordinating Group or its member agencies of any product or service to the exclusion of others that may be suitable. -
Improving Air Quality for Operators of Mobile Machines in Underground Mines
atmosphere Article Improving Air Quality for Operators of Mobile Machines in Underground Mines Andrzej Szczurek 1, Monika Maciejewska 1,*, Marcin Przybyła 2 and Wacław Szetelnicki 2 1 Faculty of Environmental Engineering, Wroclaw University of Science and Technology, Wybrze˙zeWyspia´nskiego27, 50-370 Wrocław, Poland; [email protected] 2 Centrum Bada´nJako´scisp. zo. o., ul. M. Skłodowskiej-Curie 62, 59-301 Lubin, Poland; [email protected] (M.P.); [email protected] (W.S.) * Correspondence: [email protected]; Tel.: +48-7132-028-68 Received: 12 November 2020; Accepted: 9 December 2020; Published: 18 December 2020 Abstract: In underground mines, mobile mining equipment is critical for the production system. The microenvironment inside the mobile machine may cause exposure to strongly polluted mine air, which adversely affects the health and working performance of the operator. Harmful pollutants may access the cabin together with the ventilation air delivered from the machine’s surroundings. This work proposes a solution that is able to ensure that the air for the machine operator is of proper quality. The proposal emerged from an analysis of the compliance of cabins of mobile machines working underground in mines with occupational health and safety (H&S) standards. An analytical model of air quality in a well-mixed zone was utilized for this purpose. The cabin atmosphere was investigated with regard to the concentration of gaseous species in the surrounding air, the cabin ventilation rate, and human breathing parameters. The analysis showed that if currently available ventilation approaches are used, compliance with multiple H&S standards cannot be attained inside the cabin if standards are exceeded in the surroundings of the machine. -
Indoor Air Quality
Indoor Air Quality Poor indoor air quality can cause a stuffy nose, sore throat, coughing or wheezing, headache, burning eyes, or skin rash. People with asthma or other breathing problems or who have allergies may have severe reactions. Common Indoor Air Pollutants Poor indoor air quality comes from many sources, including: » Tobacco smoke » Mold » Pollen » Allergens such as those from cats, dogs, mice, dust mites, and cockroaches » Smoke from fireplaces and woodstoves » Formaldehyde in building materials, textiles, and furniture » Carbon monoxide from gas furnaces, ovens, and other appliances » Use of household products such as cleaners and bug sprays » Outdoor air pollution from factories, vehicles, wildfires, and other sources How to Improve Indoor Air Quality » Open windows to let in fresh air. • However, if you have asthma triggered by outdoor air pollution or pollen, opening windows might not be a good idea. In this case, use exhaust fans and non-ozone-producing air cleaners to reduce exposure to these triggers. » Clean often to get rid of dust, pet fur, and other allergens. • Use a vacuum cleaner equipped with a HEPA filter. • Wet or damp mopping is better than sweeping. » Take steps to control mold and pests. » Do not smoke, and especially do not smoke indoors. If you think poor indoor air is making you sick, please see or call a doctor or other health care provider. About CDC CDC is a federal public health agency based in Atlanta, GA. Our mission is to promote health and quality of life by preventing and controlling disease, injury and disability. For More Information We want to help you to stay healthy. -
An Operational Marine Fog Prediction Model
U. S. DEPARTMENT OF COMMERCE NATIONAL OCEANIC AND ATMOSPHERIC ADMINISTRATION NATIONAL WEATHER SERVICE NATIONAL METEOROLOGICAL CENTER OFFICE NOTE 371 An Operational Marine Fog Prediction Model JORDAN C. ALPERTt DAVID M. FEIT* JUNE 1990 THIS IS AN UNREVIEWED MANUSCRIPT, PRIMARILY INTENDED FOR INFORMAL EXCHANGE OF INFORMATION AMONG NWS STAFF MEMBERS t Global Weather and Climate Modeling Branch * Ocean Products Center OPC contribution No. 45 An Operational Marine Fog Prediction Model Jordan C. Alpert and David M. Feit NOAA/NMC, Development Division Washington D.C. 20233 Abstract A major concern to the National Weather Service marine operations is the problem of forecasting advection fogs at sea. Currently fog forecasts are issued using statistical methods only over the open ocean domain but no such system is available for coastal and offshore areas. We propose to use a partially diagnostic model, designed specifically for this problem, which relies on output fields from the global operational Medium Range Forecast (MRF) model. The boundary and initial conditions of moisture and temperature, as well as the MRF's horizontal wind predictions are interpolated to the fog model grid over an arbitrarily selected coastal and offshore ocean region. The moisture fields are used to prescribe a droplet size distribution and compute liquid water content, neither of which is accounted for in the global model. Fog development is governed by the droplet size distribution and advection and exchange of heat and moisture. A simple parameterization is used to describe the coefficients of evaporation and sensible heat exchange at the surface. Depletion of the fog is based on droplet fallout of the three categories of assumed droplet size. -
Monitoring of Airborne Contamination Using Mobile Equipment
STUK-A130 FEBRUARY 1996 9- Monitoring of Airborne Contamination Using Mobile Equipment T. Honkamaa, H. Toivonen, M. Nikkinen 1 0 r 1 v. f STUK-A130 FEBRUARY 1996 Monitoring of Airborne Contamination Using Mobile Equipment T. Honkamaa, H. Toivonen, M. Nikkinen FINNISH CENTRE FOR RADIATION AND NUCLEAR SAFETY P.O.BOX 14 FIN-00881 HELSINKI Finland Tel. +358 0 759881 NEXT PAGE(S) left BLANK FINNISH CENTRE FOR RADIATION STUK-A130 AND NUCLEAR SAFETY T. Honkamaa, H. Toivonen, M. Nikkinen. Monitoring of Airborne Contamination Using Mobile Equipment. Helsinki 1996, 65 pp. ISBN 951-712-094-X ISSN 0781-1705 Key words Radioactive particles, in-field gamma-ray spectrometry, emergency preparedness ABSTRACT Rapid and accurate measurements must be carried out in a nuclear disaster that releases radioactive material into the atmosphere. To evaluate the risk to the people, .external dose rate and nuclide-specific activity concentrations in air must be determined. The Finnish Centre for Radiation and Nuclear Safety (STUK) has built an emergency vehicle to accomplish these tasks in the field. The present paper describes the systems and methods to determine the activity concentration in air. Airborne particulate sampling and gamma-ray spectrometric analysis are quantitative and sensitive tools to evaluate the nuclide-specific concentrations in air. The vehicle is equipped with a pump sampler which sucks air through a glassfiber filter (flow about 10 1 s"1). Representative sampling of airborne particles from a moving vehicle is a demanding task. According to the calculations the total collection efficiency in calm air is 60 -140% for the particle size range of 0.1 - 30 um. -
4 Air Pollution Impacts on Forests in a Changing Climate
GLOBAL ENVIRONMENTAL CHANGES 4 Air Pollution Impacts on Forests in a Changing Climate Convening lead author: Martin Lorenz Lead authors: Nicholas Clarke and Elena Paoletti Contributing authors: Andrzej Bytnerowicz, Nancy Grulke, Natalia Lukina, Hiroyuki Sase and Jeroen Staelens Abstract: Growing awareness of air pollution effects on forests has, from the early 1980s on, led to intensive forest damage research and monitoring. This has fostered air pollution control, especially in Europe and North America, and to a smaller extent also in other parts of the world. At several forest sites in these regions, there are first indications of a recovery of forest soil and tree conditions that may be attributed to improved air quality. This caused a decrease in the attention paid by politicians and the public to air pollution effects on forests. But air pollution continues to affect the structure and functioning of forest ecosystems not only in Europe and North America but even more so in parts of Russia, Asia, Latin America, and Africa. At the political level, however, attention to climate change is focussed on questions of CO2 emission and carbon sequestration. But ecological interactions between air pollution including CO2 and O3 concentrations, extreme temperatures, drought, insects, pathogens, and fire, as well as the impact of ecosystem management practices, are still poorly under- stood. Future research should focus on the interacting impacts on forest trees and ecosystems. The integrative effects of air pollution and climatic change, in particular elevated O3, altered nutrient, temperature, water availability, and elevated CO2, will be key issues for impact research. An important improvement in our understanding might be obtained by the combination of long-term multidisciplinary experiments with ecosystem-level monitoring, and the integration of the results with ecosystem modelling within a multiple-constraint framework. -
WHO Guidelines for Indoor Air Quality : Selected Pollutants
WHO GUIDELINES FOR INDOOR AIR QUALITY WHO GUIDELINES FOR INDOOR AIR QUALITY: WHO GUIDELINES FOR INDOOR AIR QUALITY: This book presents WHO guidelines for the protection of pub- lic health from risks due to a number of chemicals commonly present in indoor air. The substances considered in this review, i.e. benzene, carbon monoxide, formaldehyde, naphthalene, nitrogen dioxide, polycyclic aromatic hydrocarbons (especially benzo[a]pyrene), radon, trichloroethylene and tetrachloroethyl- ene, have indoor sources, are known in respect of their hazard- ousness to health and are often found indoors in concentrations of health concern. The guidelines are targeted at public health professionals involved in preventing health risks of environmen- SELECTED CHEMICALS SELECTED tal exposures, as well as specialists and authorities involved in the design and use of buildings, indoor materials and products. POLLUTANTS They provide a scientific basis for legally enforceable standards. World Health Organization Regional Offi ce for Europe Scherfi gsvej 8, DK-2100 Copenhagen Ø, Denmark Tel.: +45 39 17 17 17. Fax: +45 39 17 18 18 E-mail: [email protected] Web site: www.euro.who.int WHO guidelines for indoor air quality: selected pollutants The WHO European Centre for Environment and Health, Bonn Office, WHO Regional Office for Europe coordinated the development of these WHO guidelines. Keywords AIR POLLUTION, INDOOR - prevention and control AIR POLLUTANTS - adverse effects ORGANIC CHEMICALS ENVIRONMENTAL EXPOSURE - adverse effects GUIDELINES ISBN 978 92 890 0213 4 Address requests for publications of the WHO Regional Office for Europe to: Publications WHO Regional Office for Europe Scherfigsvej 8 DK-2100 Copenhagen Ø, Denmark Alternatively, complete an online request form for documentation, health information, or for per- mission to quote or translate, on the Regional Office web site (http://www.euro.who.int/pubrequest). -
Lecture 18 Condensation And
Lecture 18 Condensation and Fog Cloud Formation by Condensation • Mixed into air are myriad submicron particles (sulfuric acid droplets, soot, dust, salt), many of which are attracted to water molecules. As RH rises above 80%, these particles bind more water and swell, producing haze. • When the air becomes supersaturated, the largest of these particles act as condensation nucleii onto which water condenses as cloud droplets. • Typical cloud droplets have diameters of 2-20 microns (diameter of a hair is about 100 microns). • There are usually 50-1000 droplets per cm3, with highest droplet concentra- tions in polluted continental regions. Why can you often see your breath? Condensation can occur when warm moist (but unsaturated air) mixes with cold dry (and unsat- urated) air (also contrails, chimney steam, steam fog). Temp. RH SVP VP cold air (A) 0 C 20% 6 mb 1 mb(clear) B breath (B) 36 C 80% 63 mb 55 mb(clear) C 50% cold (C)18 C 140% 20 mb 28 mb(fog) 90% cold (D) 4 C 90% 8 mb 6 mb(clear) D A • The 50-50 mix visibly condenses into a short- lived cloud, but evaporates as breath is EOM 4.5 diluted. Fog Fog: cloud at ground level Four main types: radiation fog, advection fog, upslope fog, steam fog. TWB p. 68 • Forms due to nighttime longwave cooling of surface air below dew point. • Promoted by clear, calm, long nights. Common in Seattle in winter. • Daytime warming of ground and air ‘burns off’ fog when temperature exceeds dew point. • Fog may lift into a low cloud layer when it thickens or dissipates. -
Chapter 4: Fog
CHAPTER 4: FOG Fog is a double threat to boaters. It not only reduces visibility but also distorts sound, making collisions with obstacles – including other boats – a serious hazard. 1. Introduction Fog is a low-lying cloud that forms at or near the surface of the Earth. It is made up of tiny water droplets or ice crystals suspended in the air and usually gets its moisture from a nearby body of water or the wet ground. Fog is distinguished from mist or haze only by its density. In marine forecasts, the term “fog” is used when visibility is less than one nautical mile – or approximately two kilometres. If visibility is greater than that, but is still reduced, it is considered mist or haze. It is important to note that foggy conditions are reported on land only if visibility is less than half a nautical mile (about one kilometre). So boaters may encounter fog near coastal areas even if it is not mentioned in land-based forecasts – or particularly heavy fog, if it is. Fog Caused Worst Maritime Disaster in Canadian History The worst maritime accident in Canadian history took place in dense fog in the early hours of the morning on May 29, 1914, when the Norwegian coal ship Storstadt collided with the Canadian Pacific ocean liner Empress of Ireland. More than 1,000 people died after the Liverpool-bound liner was struck in the side and sank less than 15 minutes later in the frigid waters of the St. Lawrence River near Rimouski, Quebec. The Captain of the Empress told an inquest that he had brought his ship to a halt and was waiting for the weather to clear when, to his horror, a ship emerged from the fog, bearing directly upon him from less than a ship’s length away. -
Indoor Air Quality in Commercial and Institutional Buildings
Indoor Air Quality in Commercial and Institutional Buildings OSHA 3430-04 2011 Occupational Safety and Health Act of 1970 “To assure safe and healthful working conditions for working men and women; by authorizing enforcement of the standards developed under the Act; by assisting and encouraging the States in their efforts to assure safe and healthful working conditions; by providing for research, information, education, and training in the field of occupational safety and health.” This publication provides a general overview of a particular standards-related topic. This publication does not alter or determine compliance responsibili- ties which are set forth in OSHA standards, and the Occupational Safety and Health Act of 1970. More- over, because interpretations and enforcement poli- cy may change over time, for additional guidance on OSHA compliance requirements, the reader should consult current administrative interpretations and decisions by the Occupational Safety and Health Review Commission and the courts. Material contained in this publication is in the public domain and may be reproduced, fully or partially, without permission. Source credit is requested but not required. This information will be made available to sensory- impaired individuals upon request. Voice phone: (202) 693-1999; teletypewriter (TTY) number: 1-877- 889-5627. Indoor Air Quality in Commercial and Institutional Buildings Occupational Safety and Health Administration U.S. Department of Labor OSHA 3430-04 2011 The guidance is advisory in nature and informational in content. It is not a standard or regulation, and it neither creates new legal obligations nor alters existing obligations created by OSHA standards or the Occupational Safety and Health Act.