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A review of low-level air pollution and adverse
  REVIEW

  A review of low-level air pollution and adverse effects on human health:implications for epidemiological studies and public policy

  Neide Regina Simo?es Olmo,I Paulo Hila′rio do Nascimento Saldiva,I Alfe′sio Lu?′s Ferreira Braga,I,II,III Chin An Lin,I Ubiratan de Paula Santos,I Luiz Alberto Amador Pereira I,III

  I Laboratory of Experimental Air Pollution(LIM05),Department of Pathology,Faculdade de Medicina da Universidade de Sa?o Paulo,Sa?o Paulo,Brazil. II Environmental Pediatrics Program,University of Santo Amaro Medical School,Sa?o Paulo,Brazil.III Community Health Post-Graduation Program,Catholic University of Santos,Santos,SP,Brazil.

  The aim of this study was to review original scientific articles describing the relationship between atmospheric pollution and damage to human health.We also aimed to determine which of these studies mentioned public policy issues.Original articles relating to atmospheric pollution and human health published between1995and 2009were retrieved from the PubMed database and analyzed.This study included only articles dealing with atmospheric pollutants resulting primarily from vehicle emissions.Three researchers were involved in the final selection of the studies,and the chosen articles were approved by at least two of the three researchers.Of the84 non-Brazilian studies analyzed,80showed an association between atmospheric pollution and adverse effects on human health.Moreover,66showed evidence of adverse effects on human health,even at levels below the permitted emission standards.Three studies mentioned public policies aimed at changing emission standards. Similarly,the29selected Brazilian studies reported adverse associations with human health,and27showed evidence of adverse effects even at levels below the legally permitted emission standards.Of these studies,16 mentioned public policies aimed at changing emission standards.Based on the Brazilian and non-Brazilian scientific studies that have been conducted,it can be concluded that,even under conditions that are compliant with Brazilian air quality standards,the concentration of atmospheric pollutants in Brazil can negatively affect human health. However,as little discussion of this topic has been generated,this finding demonstrates the need to incorporate epidemiological evidence into decisions regarding legal regulations and to discuss the public policy implications in epidemiological studies.

  KEYWORDS:Air pollution;adverse effects;human health;publication bias;public policies;systematic review.

  Olmo NRS,Saldiva PHN,Braga ALF,An Lin C,Santos UP,Pereira LAA.A review of low-level air pollution and adverse effects on human health: implications for epidemiological studies and public policy.Clinics.2011;66(4):681-690.

  Received for publication on November8,2010;First review completed on December6,2000;Accepted for publication on January17,2011 E-mail:neideolmo@usp.br

  Tel.:55113061-8530

  INTRODUCTION

  Motor vehicle emissions have been increasing over time, and more efficient measures are required for their effective reduction.Among the anthropogenic sources of emissions, the present work focuses on pollution from mobile sources, primarily motor vehicles.

  It is predicted that vehicle emissions in2030will be worse than they are now.The harmful effects of vehicle pollutants (hydrocarbons,nitrogen oxide,carbon monoxide and particulates)on human health and the environment have been scientifically proven,and the body of evidence detailing these effects continues to grow.1

  Solid or suspended liquid particles,such as those present in aerosol sprays,are classified according to their aero-dynamic properties(which are the determinants of particle transportation,penetration and deposition in the respiratory airway)as follows:coarse(2.5to10m m aerodynamic diameter),fine(less than2.5m m in diameter)and ultrafine (less than0.1m m in diameter).11

  In large urban centers,people die from causes related to air pollution each year.In addition to causing deaths,air pollution is also the cause of a number of immediate, medium-term and long-term human health problems.11 Fine particles can reach the alveoli and enter the blood stream,and heart and lung disease,100diabetes,102prema-ture birth,35low birth weight,34cancer,28sudden death37 and cognitive alterations41are some of the comorbidities that have been associated with the effects of or damage caused by air pollution in large urban centers.2 According to Damasceno-Rodrigues et al.(2009),the mechanisms by which air pollution negatively influences these comorbidities are not well understood.Possible

  Copyright?2011CLINICS–This is an Open Access article distributed under

  the terms of the Creative Commons Attribution Non-Commercial License(http://

  creativecommons.org/licenses/by-nc/3.0/)which permits unrestricted non-

  commercial use,distribution,and reproduction in any medium,provided the

  original work is properly cited.

  CLINICS2011;66(4):681-690DOI:10.1590/S1807-59322011000400025

  mechanisms,such as increased calcium influx upon contact with macrophages,upregulation of proinflammatory med-iators,increased blood viscosity,increased fibrinogen and C-reactive protein levels and alterations in blood rheology favoring coagulation,have been suggested.The oxidative stress generated by air pollution has also been proposed as a major mechanism of tissue injury leading to pulmonary and systemic inflammation.124

  The World Health Organization(WHO)recommends PM2.5(particulate matter less than 2.5m m in diameter) rather than PM10(particulate matter less than10m m in diameter)as an indicator of risk to human health.4In1997, the American Environmental Agency(US EPA)established the initial parameters for PM2.5.

  Several episodes of excessive pollution have been correlated with increased numbers of deaths in some cities in Europe and the United States.5,6.The Clean Air Act of 1956and1968expanded the oversight of polluting emis-sions.In1976in Europe,the Commission of the European Communities(CEC)established standards for air quality, which were further revised and used as the basis for European legislation.7In the1950s,California implemented pioneering legal regulations controlling vehicle emissions. In2005,the WHO also established standard values for this parameter.

  In the1970s and1980s,increases in vehicle production led to a larger number of vehicles being used worldwide,a trend that was most noticeable in large urban centers.In Brazil,Resolution03/1990from the Environmental National Council(CONAMA),which used data from CONAMA Resolution05/1989,established standards for air quality consisting of‘‘the concentrations of pollution that,when exceeded,could affect the health,safety and wellbeing of the population,as well as causing damage to flora,fauna and the environment in general….’’The resolution described atmospheric pollution as‘‘any form of matter or energy with sufficient quantity,concentration,exposure or char-acteristics beyond the established levels that could cause the air to be the following:I-inadequate,harmful or damaging to health;II-inappropriate for public wellbeing;III-damaging to materials,fauna and flora;and IV-damaging to the safety,use and enjoyment of property and to the normal activities of the community.’’8

  In1998,increased emissions of pollutants in Sa?o Paulo led to the implementation of the Program for Control of Air Pollution by Motor Vehicles,PROCONVE(originally created in1986).This program declared that new vehicles should conform to the maximum emission limits under standard tests using a reference fuel.It also required certification for prototypes and production line vehicles,a special license from the federal environmental authority for the use of alternative fuels,withdrawal and repair of vehicles that did not conform to the production or project specifications and prohibition of the sales of non-homo-logated vehicles.This program led to the removal of lead from gas in1989,set22%as the proportion of anhydrous alcohol to be added to gas across the entire country in1993 and gradually reduced the sulfur content in diesel fuel used inside cities.9

  However,vehicle emissions are still the main source of atmospheric pollution,and the Brazilian standards have not changed since the1990s,when the CONAMA Resolution was published as Resolution03/1990.A number of studies have shown a clear association between atmospheric pollution and negative effects on human health,thus demonstrating the concern of the scientific community on this topic.However,despite the weight of scientific evidence,air quality standards in Brazil have remained the same over the last20years,indicating a significant imbalance between the science and public policy. Seeking a balance between individual rights(the exposure of each citizen to pollutants)and collective rights(those of society as a whole),the present study aimed to review original Brazilian and non-Brazilian studies carried out between1995and2009.By means of a systematic review, the cause-effect relationship between pollution from motor vehicles and adverse events on human health was exam-ined,both for pollution levels at legally permitted standards and those below the standards.Additionally,this review was conducted to identify whether these studies dealt with aspects of public policy involving measures to mitigate the adverse effects of pollution on human health.This outcome would suggest an interplay between the science and the adoption of public policies,thus expressing intersectoral attempts to protect our greatest asset,human health. Consequently,the hypothesis investigated in this review is that the interface between law and epidemiology is necessary for and capable of protecting human health from the effects of pollution.From this starting point,our work aimed to assist decision makers in discussing more restrictive proposals for air quality standards,following international trends.Furthermore,the present study not only reviewed data from epidemiological studies but also investigated which studies specifically assessed the data with respect to concerns for developing efficient public policy.

  METHODS

  PubMed was used for this review because it includes over 19million papers from health-related fields that were published in over3,800scientific journals.Furthermore, papers in the PubMed database include studies from other primary sources,such as Medline,meaning that PubMed includes a large number of both Brazilian and non-Brazilian reports published in internationally renowned scientific journals.PubMed was developed by the National Center for Biotechnology Information,and it is maintained by the National Library of Medicine.

  The following terms were used for searching the PubMed database:

  N air pollution,health,Brazil,epidemiologic;

  N air pollution,health,Brazil;

  N air pollution,health,Brazil,epidemiologic study;

  N air pollution,health,epidemiologic cohort;

  N air pollution,health,epidemiologic case control;

  N air pollution,health,epidemiologic time series study; N traffic,air pollution,epidemiologic panel;

  N traffic,air pollution,epidemiologic review.

  Original studies were initially selected for our analysis after excluding those in which the objectives did not include vehicle atmospheric pollution(for example,papers on pollution due to sugar cane burning or papers regarding internal pollutants).

  A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  CLINICS2011;66(4):681-690

  At the next stage,three researchers were invited to choose epidemiological studies using their own judgment,based on experience,with the aim of addressing the study hypothesis presented above.The researchers separately made decisions regarding the inclusion of the studies to avoid bias in the inclusion criteria.The researchers were epidemiologists and experts on atmospheric pollution,and the studies were selected based on their epidemiological quality.Each of the reviewers received a file containing full reprints of the epidemiological studies,as well as a list of all study titles divided according to study type.After making their selections through an analysis of the basis and methodolo-gical quality of the studies,the researchers returned the file and titles.

  The studies selected were those that received at least two votes for inclusion in the systematic review and that referred to outdoor air pollution,particularly the ones related to atmospheric emission of pollutants from motor vehicles.Only national and international studies related to air pollution in peer-reviewed journals,epidemiological studies,original articles and studies examining automotive sources of outdoor pollution with well-explained statistical positive or negative associations were included.

  The final selection was made by the study supervisor, who reviewed all of the articles according to the inclusion criteria.

  Two tables containing the following data were prepared: type of study,study design,outcome,study population, statistical analysis applied,pollutants investigated,esti-mates,covariables and whether the effects on health were assessed,including cases where the levels were below the legally permitted standards.One table included Brazilian papers,whereas the other included non-Brazilian studies. The data from these initial tables were used to produce two additional tables that are presented in this paper.These tables include only the type of study,study population, outcome,association,discussion of public policies for decreasing pollution levels,effects on health if emissions

  remain below the Brazilian standards and the appropriate citation(s)for each study.

  The scientific papers selected for this work were original, but any review articles and systematic review papers found were used for data comparison and discussion.

  In addition,two figures showing the percentage increase in pollution,including cases where it was below the limits imposed by air quality standards,were designed.These figures present the percentage increases and their con-fidence intervals.

  RESULTS

  Initially,2,530Brazilian and non-Brazilian articles were collected,and after preliminary selection,249articles exclusively referring to outdoor pollution were chosen. After the subsequent analysis conducted by the three researchers participating in the study group,143reports were finally selected according the inclusion criteria described in the Methods section.

  Only113of these articles were used in our final analysis because reviews and systematic reviews were excluded. Figure1shows the selection steps in the review process. The non-Brazilian studies selected included1clinical trial, 9case crossover studies,13case-control studies,15time series,28cohorts,10panels,22reviews,6systematic reviews and8cross-sectional studies.Therefore,a total of 112non-Brazilian studies were included.Excluding reviews and systematic reviews,84non-Brazilian studies remained for our final analysis(Table1).

  The Brazilian studies selected included1case control,2 panels,2reviews,20time series and6cross-sectional studies.Therefore,a total of31Brazilian studies were included,and excluding reviews and systematic reviews,29 Brazilian studies remained for our final analysis(Table2). Of the84non-Brazilian studies selected for our analysis (excluding reviews and systematic reviews),66demon-strated effects on health,even when emissions were below the permitted levels(these studies are marked‘‘yes’’in the corresponding column in Table1).These66non-Brazilian studies demonstrated that,even when emissions of atmo-spheric pollutants were below the levels permitted by Brazilian legislation,they were capable of negatively affecting the health of the urban population.

  Among the30Brazilian studies selected for the present work(excluding reviews),27showed that there were risks to health,even if the population was exposed to pollution levels below those permitted by Brazilian legislation.

  The reviewed studies showed that some age groups, particularly the elderly and children,are more susceptible to air pollution emissions.Some diseases were frequently associated with exposure to air pollution;for

  example, Figure1-Selection steps in the review process.

  CLINICS2011;66(4):681-690A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  respiratory and cardiovascular outcomes were described in several studies (Tables 1and 2).

  Only 3of the non-Brazilian studies and 16of the Brazilian studies specifically mentioned public policy.

  Finally,Figures 2and 3show the percentage increase of some of the endpoints of the selected studies and their relative risks.

  DISCUSSION

  Although the papers selected for review in this study have associated atmospheric pollutants with damage to human health,including comorbidities such as respiratory diseases,cardiovascular diseases,pregnancy outcomes,cancer and death,most of these papers failed to mention public policy.Therefore,while science is making great

  strides in demonstrating the harmful effects of atmospheric pollution on human health,public authorities are not using these data to make decisions concerning the reduction of emissions or the adoption of measures that might indirectly affect the comfort of the population and,therefore,might not be politically acceptable.Nonetheless,such measures should be adopted,together with an awareness campaign,so that a change of habits and attitudes occurs in everyday lives.

  Epidemiological evidence produced using several differ-ent study models has demonstrated that atmospheric pollution negatively affects human health,even if the pollutants are below the levels established by Brazilian legislation (CONAMA National Council of the Environment Resolution 03/1990).However,despite the available scien-tific evidence,there has still not been any appropriate

  Table 1-Non-Brazilian studies of air pollution,categorized by type of study,study population,outcomes and effects found.

  Type of study (n )Study population (n )Outcome (n )Association (n )

  Effect below the Brazilian limit (n )

  Discussion on public policies for decreasing

  emissions References

  Clinical trial (1)Adults (1)Atherosclerosis Yes Yes (1)No (1)16Case crossover (9)Adults (5)Children (1)Respiratory diseases (4)

  Yes (8)Yes (8)No (9)

  17-25

  Elderly (2)Cardiovascular diseases (5)No (1)No (1)All (1)

  Case control (13)Adult (5)Respiratory diseases (4)

  Yes (11)Yes (7)No (13)26-38

  Children (7)Pregnancy-related outcomes

  (3)

  No (2)

  No (6)

  Elderly (1)Cardiovascular diseases (3)

  Cancer (3)

  Cohort (28)Adults (12)Respiratory diseases (8)

  Yes (28)

  Yes (22)

  No (28)39-66

  Children (13)Mortality (3)No (6)

  Elderly (3)Pregnancy-related outcomes

  (3)

  Cognitive deficit (1)

  Cancer (1)Otitis (1)

  Cardiovascular diseases (11)

  Panel (10)Adults (5)Respiratory diseases (5)

  Yes (9)Yes (9)Yes (2)67-76

  Children (3)Cardiovascular diseases (5)No(1)No (1)No (8)Elderly (2)

  Time series (15)Adults (13)Respiratory diseases (1)

  Yes (15)

  Yes (15)

  Yes (1)77-91

  Elderly (1)Cardiovascular diseases (3)No (14)All (1)Mortality (11)

  Cross-sectional (8)Adults (5)Respiratory diseases (6)

  Yes (8)

  Yes (4)No (8)

  92-99

  Children (2)Cardiovascular diseases (1)No (4)

  Elderly (1)Diabetes (1)n =quantity.

  Table 2-Brazilian studies of air pollution,categorized by type of study,study population,outcomes and effects found.

  Type of study (n )Study population

  (n )Outcome (n )Association (n )Effects below the Brazilian limit (n )Discussion on public policies for decreasing

  emissions

  References Case control (1)

  Children (1)Perinatal death Yes

  Not informed

  Not informed

  100Panel (2)

  Adults (1)Blood pressure;carboxyhemoglobin Yes for both

  Yes (2)

  Yes (1)101–102

  Children (1)No (1)Time series (20)

  Adults (7)Respiratory diseases (14);Yes (19)Yes (18)Yes (12)103-123

  Children (11)Pregnancy-related outcomes

  (2);

  No (1)No (2)

  No (8)

  Elderly (2)Cardiovascular diseases (4)Cross-sectional (6)

  Children (5)Respiratory diseases (4)Yes (5)Yes (6)

  Yes (3)124-129

  All (1)

  Child mortality (1)

  No (1)

  No (3)

  Pregnancy-related outcomes (1)

  n =quantity.

  A review of low-level air pollution and adverse effects on human health Olmo NRS et al.

  CLINICS 2011;66(4):681-690

  reaction in terms of the adoption of public policies in Brazil that are aimed at improving the air quality of large urban centers.

  Measures such as vehicle inspections,efficient public transport,traffic management,bus lanes,bicycle lane systems and urban tolls are all consistent with proposals for creating a healthy environment.However,the use of cleaner fuel must also be pursued because sustained sulfur emissions will lead to more deaths and hospitalizations.

  Studies carried out at the University of Sa

  ?o Paulo have confirmed that living in a city with polluted air leads to a 75%increase in the risk of a heart attack compared to living in a city with clean air.Additionally,the possibility of dying in a traffic jam is two and a half times greater in a polluted city.For every 10m g/m 3of PM 10removed from the air,there is an increase in life expectancy of eight to twelve months.If an economic model was applied to Brazilian public health,and the well-being of the population and quality of life were considered,it would reveal how much Brazil is losing,even though a few companies and decision makers may still be turning profits.

  According to Dockery and Pope,10the establishment of emission standards implies the existence of a limit below which there would be no harm to health.However,in reality,the response is linear,and there is no safe lower limit of these pollutants in terms of human health.

  Despite ample scientific evidence,no strong concern has been shown for human health and its sensitivity to pollution.In Brazil,we have been using outdated standards that do not follow the international trend.Moreover,we have adopted policies that encourage the purchase of vehicles and,thus,are inadequate to solve transportation problems.At the same time,the use of diesel fuel,which causes less pollution,has been postponed.In conclusion,Brazil needs to change its emission standards and adopt policies that address the awareness,expansion and improvement of public transportation.

  The present review highlights the inappropriate nature of decisions made by public institutions regarding the estab-lishment of public policies related to pollution,which are dissociated from the reality demonstrated by scientific evidence.Therefore,the authors of this report seek to draw the attention of Brazilian decision makers toward imple-menting changes in the public and political measures adopted on this topic.Epidemiological studies need to be understood and used as the basis for defining these public policies with the aim of improving the quality of life among the target population.Education,awareness and concern are allies in the adoption of appropriate public policies.Of the 113Brazilian and non-Brazilian articles that were analyzed in the present review,only 4papers did not find an association between pollution and health.This suggests that there may be a publication bias.Such a bias would consist of a tendency for researchers,reviewers and editors to only submit or accept papers that follow the direction of the hypothesis that they wish to prove.It is important and necessary to avoid publication biases,both from the point of view of the universal nature of scientific knowledge and of meta-analysis studies.Decisions regarding treatments,medications placed on the market and many

  medical

  Figure 2-Percentage increase interval (CI 95%)from selected non-Brazilian studies of air pollution and adverse human health outcomes.

  CLINICS 2011;66(4):681-690

  A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  situations and public health decisions are based on research.14However,there is strong evidence supporting the association between atmospheric pollution by vehicles and adverse effects on human health.

  The tables presenting the summarized data from the papers selected not only show the cause-effect relationship between atmospheric pollution and harm to human health but also indicate which of the selected studies effectively led to attitudes being adopted in terms of public policy.From the perspective of proposals for public policy,there is a gap between the science and the policy makers because even the studies that mention public policy do not actually suggest proposals for reducing atmospheric pollution.

  By bringing together studies from several parts of the world,including Brazil,it can be seen that their results trend in the same direction.The studies were able to answer the essential questions proposed in the present study,namely:Is there any epidemiological evidence for adverse effects of atmospheric pollution on human health?Do these effects occur even at concentrations that are lower than the maximum permitted levels?Was there any concern in these reports about outlining public policy measures that would restrict emissions?The present work produced clear answers to these questions.There is epidemiological evidence for the negative effects of atmospheric pollution on human health,and these effects can be observed even after exposure to emission levels that are below the established legal levels in Brazil.The most-affected population comprises so-called susceptible indivi-duals (children,the elderly and individuals with heart disease or asthma).Few reports specifically mentioned public health policy,but it seems that mentioning such policies is more frequent in Brazilian studies than in non-Brazilian ones.The Brazilian model for individual transportation is failing,and there is a need to prioritize and modernize the public transportation system.Even if public health were not an issue,the time wasted in traffic jams should be a motivating factor for adopting new public policies and changing the habits of the population.Thus,the immobili-zation of urban centers will force decision makers and people living in the city to become aware of these issues.The adoption of more efficient public policies is essential for the reduction of current emission standards for air pollutants.These measures cannot continue to accommo-date an increasing number of vehicles.Instead,epidemiol-ogy should be seen as a science advocating the adoption of stricter standards for air emissions as well as education of the population involved,thereby giving legitimacy to its decisions.Thus,policies on education,awareness and mandatory investments in the automotive sector and in public transportation are of paramount importance to accomplish this goal.Internationally,priority is given to scientific information and to active public participation,not only as consumers but also as an essential part of the quality of life,both present and future.Such participation requires the adoption of integrated measures based on the popula-tion and the

  government.

  Figure 3-Percentage increase interval (CI 95%)from Brazilian studies of air pollution and adverse human health outcomes.

  A review of low-level air pollution and adverse effects on human health Olmo NRS et al.

  CLINICS 2011;66(4):681-690

  Therefore,we hope that this work can serve as the basis for a dynamic and responsible decision-making process.We also hope that it can be used to establish public policies that are not only theoretically ideal but also equally efficient regarding human health.

  CONCLUSION

  This review made it possible to extrapolate conclusions from the individual and independent results of each study analyzed,identifying coherent data that can be used for developing public guidelines and for future planning.The present study used scientific data based on epidemiological studies that were produced both within the Brazilian sphere and in other countries.It showed that,even when atmospheric pollutants are within legally established limits,they can be harmful to health.This harm leads to additional expenses for public health services and,ulti-mately,for the government,which is responsible for ensuring the quality of life of the population and assuring the right to healthcare.

  The concept of co-benefits of pollution control is becoming increasingly relevant and is taking on the role of a guiding principle because there must be synergy between the measures aimed at the mitigation of emissions and those aimed at improving public health.These concepts are constantly interlinking the fields of healthcare and law and can lead to public policies based upon scientifically verified results.Such policies always aim toward a better quality of life and increased well-being of the population.

  The aim of this study was not to explain the pathophy-siology of the comorbidities caused by exposure to air pollutants.However,considering the harmful effects that have already been reported in epidemiological studies(such as those that were part of this systematic review,listed in Tables1and2),we discussed the need for the application of these data by decision makers to allow for the proper adjustment of legislation in support of human health.Thus, epidemiological studies were used as a tool to demonstrate the objective of this paper,namely the need for an interrelationship between health and epidemiology in the shaping of Brazilian public policy.

  Finally,we suggest an interface between science and Brazilian public policy involving intersectoral attempts to protect our most important asset,human health.

  This study was supported by the Laboratory of Medical Investigations(LIM05-FMUSP)and FAPESP(Research Support Foundation of the State of Sa?o Paulo). ACKNOWLEDGEMENTS

  We are grateful to the LIM05-FMUSP(Laboratory for Medical Investigations of the University of Sa?o Paulo)for its unwavering support and to the Research Support Foundation of the State of Sa?o Paulo (FAPESP)for the study bursary that made this work possible. REFERENCES

  1.Memorandum de Bellagio sobre Pol?′ticas Automotivas.Princ?′pios para

  Ve?′culos e combust?′veis perante Imperativos Mundiais de Meio Ambiente e Sau′de(in Portuguese).Documento consenso19-21de junho,2001,Bellagio,Ita′lia.

  2.CETESB,Relato′rio de Qualidade do Ar2008.(in Portuguese).http://

  www.cetesb.sp.gov.br/publicacoes/publicacoes.asp(accessed in dec/ 2009).

  3.Marcilio I,Gouveia N.Quantifying the Impact of air pollution on the

  Urban population of Brazil.Cad.Sau′de Pu′blica,Rio de Janeiro,23Sup 4:S529-S536,2007.

  4.World Health Organization WHO.Media Center.Particulate Matter,

  Guidelines values.http://www.who.int/mediacentre/multimedia (accessed in dec/2009).

  5.Firket J.The Problem of Cancer of the Lung in the Industrial Area of

  Lie′ge During Recent Years.Section of Pathology.Proceedings of the Royal Society of Medicine.Jan.1958.

  6.Logan WP.Mortality in the London fog incident,1952.Lancet.

  1953;17:336-8,doi:10.1016/S0140-6736(53)91012-5.

  7.United States Environmental Protection Agency US EPA.http://

  www.epa.gov/ttn/naaqs(accessed on dec/2009).

  8.Resoluc?a?o CONAMA03/1990.(in Portuguese).http://www.mma.

  gov.br/conama.(accessed in dec/2009).

  9.Programa de Controle da Poluic?a?o do Ar por Ve?′culos Automotores–

  PROCONVE/Ministe′rio do Meio Ambiente e dos Recursos H?′dricos e da Amazo?nia Legal,Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renova′veis(in Portuguese).2ed.Bras?′lia:IBAMA, 1998.

  10.Planeta Sustenta′vel.(in Portuguese).http://planetasustenta′vel.abril.

  com.br/noticia/ambiente/conteu′do_305523.shtml.(accessed in dec/2009).

  11.Pope III CA,Dockery DW.Health Effects of Fine Particulate Air Pollution:

  Lines that Connect.Air&Waste Manage Assoc.2006;56:709-42.

  12.Dickersen K.The Existence of Publication Bias and Risk Factors for its

  Occurrence.Jama.1990;263:1385-59,doi:10.1001/jama.263.10.1385. 13.Luber G,Prudent N.Climate Change and Human Health.Trans Am

  Clin Climatol.Assoc.2009;120:113-7.

  14.Kunzli N,Jerrett M,Mack WJ,Bekerman B,LaBree L,Gilliland F,et al.

  Ambient Air Pollution and Atherosclerosis in Los Angeles.Environmental Health Perspectives.2005;113:201-6,doi:10.1289/ehp.7523.

  15.Symons JM,Wang L,Guallar E,Howell E,Dominici F,Schwab M,et al.

  A Case Crossover study of Fine Particulate Matter Air pollution and

  Onset of Congestive Heart Failure Symptom Exacerbation Leading to Hospitalization.Am J Epidemiol.2006;164:421-33.

  16.Barnett AG,Williams GM,Schwartz J,Neller AH,Best TL,

  Petroeschevsky,et al.Air Pollution and Child Respiratory Health.

  Am J Respr Crit Care Med.2005;171:1272-8,doi:10.1164/rccm.200411-1586OC.

  17.Kim SY,O’Neill MS,Lee JT,Cho Y,Kim J,Kim H.Air Pollution,

  Socioeconomic Position,and Emergency Hospital Visits for Asthma in Seoul,Korea.Int Arch Occup Environ Health.2007;80:701-10,doi:10.

  1007/s00420-007-0182-3.

  18.McCreanor J,Cullinan P,Nieuwenhuijsen MJ,Evans JS,Malliarou E,

  Jarup L,et al.Respiratory Effects of Exposure to Diesel Traffic in Persons with Asthma.N Engl J Med.2007;357:2348-58.

  19.Zanobetti A,Schwartz J.The Effects of Particulate Air Pollution on

  Emergency Admissions for Myocardial infarction:A Multicity Case Crossover Analysis.Environmental Health Perspectives.2005;113:978-82,doi:10.1289/ehp.7550.

  20.Barnett AG,Williams GM,Schwartz J,Bes TL,Neller AH,

  Petroeschevsky AL,et al.The Effects of Air Pollution on Hospitalizations for Cardiovascular Disease in Elderly People in Australian and New Zealand Cities.Environmental Health Perspectives.2006;114:1018-23,doi:10.1289/ehp.8674.

  21.Zanobetti A,Schwartz J.Air Pollution and Emergency Admissions in

  Boston,MA.J Epidemiol Community Health.2006;60:890-5,doi:10.

  1136/jech.2005.039834.

  22.Peters A,Klot S,Heier M,Trentinaglia I,Cyrys J,Ho¨rmann A,et al.

  Particulate Air Pollution and Nonfatal Cardiac Events Part I.Health Effects Institute Research Report.2005;124:1–66.

  23.Peel JL,Metzger KB,Klein M,Flanders WD,Mulholland JA,Tolbert PE.

  Ambient Air Pollution and Cardiovascular Emergency Department Visits in Potentially Sensitive Groups.Am J Epidemiol.2007;165:625-33.

  24.Tonne C,Melly S,Mittleman M,Coull B,Goldberg R,Schwartz.A Case

  Control Analysis of Exposure to Traffic and Acute Myocardial Infarction.Environmental Health Perspectives.2007;115:53-7,doi:10.

  1289/ehp.9587.

  25.Ritz B,Wilhelm M,Zhao Y.Air Pollution and Infant Death in Southern

  California1989-2000.Am Ac Pediatrics2006;118:493-502.

  26.Rogers J,Dunlop AL.Air Pollution and Very Low Birth Weight Infants;

  A target Population.Am Ac Pediatrics.2006;118:156-64.

  27.Migliaretti G,Dalmasso P,Gregorio D.Air Pollution Effects on the

  Respiratory Adult Population in Turin,Italy.Int J Environ Health Research.2007;175:369-79,doi:10.1080/09603120701628768.

  28.Nielsen OR,Hertel O,Thomsen BL,Olsen JH.Air Pollution from Traffic

  at the Residence of Children with Cancer.Am J Epidemiol.

  2001;153:433-43.

  29.Weng H,Tsai SS,Chiu HF,Wu TN,Yang CY.Childhood Leukemia and

  Traffic Air Pollution in Taiwan;Petrol Station Density as an Indicator.

  J Toxicol Environ Health.2009;72:83-7,doi:10.1080/15287390802477338.

  30.Baccarelli A,Martinelli I,Zanobetti A,Grillo P,Hou LF,Bertazzi PA,

  et al.Exposure to Particulate Air Pollution and Risk of Deep Vein

  CLINICS2011;66(4):681-690A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  Thrombosis.Arch Intern Med.2008;168;920-27,doi:10.1001/archinte.

  168.9.920.

  31.Nie J,Beyea J,Bonner MR,Han D,Vena JE,Rogerson P,et al.Exposure

  to Traffic Emissions Throughout Life and Risk of Breast Cancer:The Western New York Exposures and Breast Cancer(WEB)Study.Cancer Causes Control.2007;18:947-55,doi:10.1007/s10552-007-9036-2.

  32.Rosenlund M,Berglind N,Pershagen G,Hallqvist J,Jonson T,Bellander

  T.Long Term Exposure to Urban Air Pollution and Myocardial Infarction.Epidemiology.2006;17;383-90,doi:10.1097/01.ede.

  0000219722.25569.0f.

  33.Villeneuve P,Chen L,Rowe B,Coates F.Outdoor Air Pollution and

  Emergency Department Visits for Asthma among Children and Adults:

  A Case Crossover Study in Northern Alberta,Canada.Environ Health.

  2007;6:40-55,doi:10.1186/1476-069X-6-40.

  34.Modig L,Ja¨rvholm B,Ro¨nnmark E,Nystro¨m,Lundback B,Andersson

  C,et al.Vehicle Exhaust Exposure in an Incident Case Control study of Adult Asthma.European Respiratory J.2006;28:75-80,doi:10.1183/ 09031936.06.00071505.

  35.Wilhem M,Ritz B.Residential Proximity to Traffic and Adverse Birth

  Outcomes in Los Angeles Country California,1994-1996.

  Environmental Health Perspectives.2003;114:207-16.

  36.Huynh M,Woodruff TJ,Parker JD,Schoendorf KC.Relation Between

  Air Pollution and Preterm Birth in Califronia.J Compilation.

  2006;20:454-61.

  37.Brauer M,Lencar C,Tamburic L,Koehoorn M,Demers Paul,Karr C.A

  Cohort Study of Traffic Related Air Pollution Impacts on Birth Outcomes.Environmental Health Perspectives.2008;116:680-6,doi:10.

  1289/ehp.10952.

  38.Kaiser R,Romieu I,Medina S,Schawartz J,Krzyzanowski M,Ku¨nzli N.

  Air Pollution Attributable Postneonatal Infant Mortality in U S Metropolitan Areas:A risk Assessment Study.Environ Health.

  2004;3:1-4,doi:10.1186/1476-069X-3-4.

  39.Brauer M,Hoek G,Vliet V,Meliefste K,Fisher PH,Wijga A,et al.Air

  Pollution from Traffic and the Development of Respiratory Infections and Asthmatic and Allergic Symptoms in Children.Am J.Respir Crit Care Med.2002;166:1092-8,doi:10.1164/rccm.200108-007OC.

  40.von Klot S,Peters A,Aalto P,Bellander T,Berglind N,D’Ippoliti D,et al.

  Ambient Air Pollution is Associated with Increased Risk of Hospital Cardiac Readmissions of Myocardial Infarction Survivors in Five European Cities.Circulation.2005;112:3073-9,doi:10.1161/ CIRCULATIONAHA.105.548743.

  41.Hoek G,Brunekreef B,Goldbohm S,Fisher P,Brandt PA van den.

  Association between Mortality and Indicators of Traffic Related Air Pollution in the Netherlands:a Cohort Study.Lancet.2002;360:1203-09, doi:10.1016/S0140-6736(02)11280-3.

  42.Suglia SF,Gryparis A,Wright RO,Schwartz J,Wright RJ.Association of

  Black Carbon with Cognition among Children in a Prospective Birth Cohort Study.Am J Epidemiol.2008;167:280-6.

  43.Schikowski T,Sugiri D,Ranft U,Gehring U,Heinrich J,Wichmann HE,

  et al.Does Respiratory Health Contribute to the Effects of Long Term Air Pollution Exposure on Cardiovascular Mortality.Respiratory Research.2007;8:1-20,doi:10.1186/1465-9921-8-20.

  44.Picciotto I,Baker R,Yap P,Dosta′l M,Joad JP,Lipsett M,et al.Early

  Chilhood Lower Respiratory Illness and Air Pollution.Environmental Health Perspectives.2007;115:1510-8.

  45.Park S,O’Neill MS,Vokonas P S,Sparrow D,Schwartz J.Effects of Air

  pollution on Heart Rate Variability;The VA Normative.Environmental Health Perspectives.2005;113:304-309,doi:10.1289/ehp.7447.

  46.Peters A,Perz S,Do¨ring A,Stieber J,Koening W,Wichmann E.

  Increases in Heart Rate During an Air Pollution Episode.

  Am J Epidemiol.1999;150:1094-8.

  47.Oglesby LB,Schindler C,Hazenkamp ME,Fahrla¨nder CB,Keidel D,

  Rapp R,et al.Living Near Main Streets and Respiratory Symptoms in Adults The Swiss Cohort Study on Air Pollution and Lung Diseases in Adults.Am J Epidemiol.2006;164:1190-8.

  48.Nafstad P,Ha¨heim LL,Oftedal B,Gram F,Holme I,Hjermann I,et al.

  Lung Cancer and Air Pollution:a27Year Follow Up of16209 Norwegian Men.Thorax.2003;58:1071-6,doi:10.1136/thorax.58.12.

  1071.

  49.Krewski D,Burnett R,Jerrett M,Pope CA,Rainham D,Calle E,et al.

  Mortality and Long Term Exposure to Ambient Air pollution:Ongoing Analyses Based on the American Cancer Society Cohort.J Toxicology Environ Health.2005;68:1093-109,doi:10.1080/15287390590935941. 50.Zanobetti A,Bind MAC,Schwartz J.Particulate Air Pollution and

  Survival in a COPD Cohort.J Environ Health.2008;7:1-9.

  51.Zanobetti A,Schwartz J.Particulate Air Pollution,Progressive and

  Survival after Myocardial Infarction.Environmental Health Perspectives.2007;115:769-75,doi:10.1289/ehp.9201.

  52.Kan H,Heiss G,Rose K,Whitsel EA,Lurmann F,London S J.

  Prospective Analysis of Traffic Exposure as a Risk Factor for Incident Coronary Heart Disease;The atherosclerosis Risk in Communities

  (ARIC)Study.Environmental Health Perspectives.2008;116:1463-68, doi:10.1289/ehp.11290.

  53.Morgenstern V,Zutavern A,Cyrys J,Brockow I,Gehring U,Koletzko S,

  et al.Respiratory Health and Individual Estimated Exposure to Traffic Related Air Pollutants in a Cohort of Young Children.Occup Environ Med.2007;64:8-16,doi:10.1136/oem.2006.028241.

  54.Dugandzic R,Dodds L,Stieb D,Doiron MS.The Association Between

  Low Level Exposures to Ambient Air Pollution and Term Low Birth Weight:A Retrospective Cohort Study.Environ Health.2006;5:1-8,doi:

  10.1186/1476-069X-5-3.

  55.Finkelstein M M,Jerrett M,Sears M.Traffic Air Pollution and Mortality

  Rate Advancement Periods.Am J Epidemiol.2004;160:173-7.

  56.Jerrett M,Shankardass K,Berhane K,Auderman WJ,Ku¨nzli N,Avol E,

  et al.Traffic Related Air Pollution and Asthma Onset in Children;a Prospective Cohort Study with Individual Exposure Measurement.

  Environmental Health Perspectives.2008;116:1433-8,doi:10.1289/ehp.

  10968.

  57.Nordling E,Berglind N,Mele′n E,Emenius G,Hallberg J,Nyberg F,et al.

  Traffic Related Air Pollution and Childhood Respiratory Symptoms, Function and Allergies.Epidemiology.2008;19:401-8,doi:10.1097/EDE.

  0b013e31816a1ce3.

  58.Brauer M,Gehring U,Brunekreef B,Jongste J,Gerritsen J,Rovers M,

  et al.Traffic Related Air Pollution and Otitis Media.Environmental Health Perspectives2006;114:1414-8,doi:10.1289/ehp.9089.

  59.Gehring U,Cyrys J,Sedlmeir G,Bunekreef B,Bellander T,Fischer P,

  et al.Traffic Related Air Pollution and Respiratory Health During the First2Yrs of Life.Eur Respr.2002;19:690-8,doi:10.1183/09031936.02.

  01182001.

  60.Rosenlund M,Picciotto S,Forastiere F,Stafoggia M,Perucci C A.Traffic

  Related Air Pollution in Relation to Incidence and Prognosis of Coronary Heart Disease.Epidemiology.2008;19:121-8,doi:10.1097/ EDE.0b013e31815c1921.

  61.Slama R,Morenstern V,Cyrys J,Zutavern A,Herbarth O,Wichmann

  HE,et al.Traffic Related Atmospheric Pollutants Levels during pregnancy and Offspring’s Term Birth Weight;A Study Relying on a Land Use Regression Exposure Model.Environmental Health Perspectives.2007;115:1283-92,doi:10.1289/ehp.10047.

  62.Nafstad P,Haheim LL,Wisloff T,Gram F,Oftedal B,Holme I,et al.

  Urban Air Pollution and Mortality in a Cohort of Norwegian Men.

  Environmental Health Perspectives.2004;112:610-5,doi:10.1289/ehp.

  6684.

  63.Shima M,Nitta Y,Adalchi M.Traffic Related Air pollution and

  Respiratory Symptoms in Children Living Along trunk Roads in Chiba Prefecture,Japan.J Epidemiology.2003;13:108-19.

  64.Gehring U,Heinrich J,Kra¨mer U,Grote V,Hochadel M,Sugiri D,et al.

  Long Term exposure to Ambient Air Pollution and Cardiopulmonary Mortality in Women.Epidemiology2006;17:545-51,doi:10.1097/01.ede.

  0000224541.38258.87.

  65.Dales R,Chen L,Frescura AM,Liu L,Villeneuve PJ.Acute Effects of

  Outdoor Air Pollution on FEV1:A Panel Study of Schoolchildren with Asthma.European Respiratory J.2009.

  66.Zanobetti A,Cnner M,Stone P,Schwartz J,Sher D,Bengston EE,et al.

  Ambient Pollution and Blood Pressure in Cardiac Rehabilitation Patients.J Am Heart Ass.2004;110:2184-9.

  67.Yue W,Schneider A,Sto¨lzel M,Ru¨ckerl R,Cyrys J,Pan X,et al.Ambient

  Source Specific Particles are Associated with Prolonged Repolarization and Increased Levels of Inflammation in Male Coronary Artery Disease Patients.Mutation Research.2007;621:50-60,doi:10.1016/j.mrfmmm.

  2007.02.009.

  68.Mulli AI,Timonen KL,Peters A,Heinrich J,wo¨lke G,Lanki T,et al.Effects

  of Particulate Air Pollution on Blood Pressure and Heart Rate in Subjects with Cardiovascular Disease:A Multicenter Approach.Environmental Health Perspectives.2004;112:369-77,doi:10.1289/ehp.6523.

  69.Moshammer H,Hutter HP,Hauck H,Neuberger M.Low levels of Air

  Pollution Induce Changes of Lung Function in a Panel of Schoolchildren.European Respiratory J.2006;27:1138-43,doi:10.1183/ 09031936.06.00089605.

  70.Schwartz J,Litonjua A,Suh H,Verrier M,Zanobetti A,Syring M,et al.

  Traffic Related Pollution and Heart Rate Variablility in a Panel of Elderly Subjects.Thorax.2005;60:455-61,doi:10.1136/thx.2004.024836.

  71.Ingle ST,Pachpande BG,Wagh ND,Patel VS,Attarde SB.Exposure to

  Vehicular Pollution and Respiratory Impairment of Traffic Policemen in Jagaon City,India.Industrial Health.2005;43:656-62,doi:10.2486/ indhealth.43.656.

  72.Gibson HL,Suh HH,Coull B,Dockery DW,Sarnat SE,Schwartz J,et al.

  Short Term Effects of Air Pollution on Heart Rate Variability in Senior Adults in Steubenville,Ohio.J Occup Environ Med.2006;48:780-8,doi:

  10.1097/01.jom.0000229781.27181.7d.

  73.Lee JT,Son JY,Cho YS.The Adverse Effects of Fine Particle Air

  Pollution on Respiratory Function in the Elderly.Science of Total Environment.2007;385:28-36,doi:10.1016/j.scitotenv.2007.07.005.

  A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  CLINICS2011;66(4):681-690

  74.Steerenberg PA,Nierkens S,Fischer PH,Loveren HV,Opperhuizen A.

  Archives of Environmental Health.2001;56:167-74.

  75.Middleton N,Yiallouros P,Kleanthous S,Kolokotroni O,Schwartz J,

  Dockery DW,et al.A10Year Time Series Analysis of Respiratory and Cardiovascular Morbidity in Nicosia,Cyprus:The Effects of Short Term Changes in Air Pollution and Dust Storms.Environ Health.2008;7:39, doi:10.1186/1476-069X-7-39.

  76.Fusco D,Forastiere F,Michelozzi P,Spadea T,Ostro B,Arca`M,et al.Air

  Pollution and Hospital Admissions for Respiratory Conditions in Rome, Italy.Eur Respir J.2001;17:1143-50,doi:10.1183/09031936.01.00005501.

  77.Cakmak S,Dales RE,Vidal CB.Air Pollution and Mortality in Chile:

  Susceptibility Among the Elderly.Environmental Health Perspectives.

  2007;115:524-7,doi:10.1289/ehp.9567.

  78.Peters A,Skorkvsky J,Kotesovec F,Brynda J,Spix C,Wichmann H E,

  et al.Associations between Mortality and Air Pollution in Central Europe.Environmental Health Perspectives.2000;108:283-7,doi:10.

  1289/ehp.00108283.

  79.Braga ALF,Zanobetti A,Schwartz J.Do Respiratory Epidemics

  Confound the Association Between Air Pollution and Daily Deaths.

  Eur Respir J.2000;16:723-8,doi:10.1034/j.1399-3003.2000.16d26.x. 80.Ostro B,Broadwin R,Green S,Feng W Y,Lipsett M.Fine Particulate Air

  pollution and Mortality in Nine California Countries:Results from CALFINE.Environmental Health Perspectives.2006;114:29-33,doi:10.

  1289/ehp.8335.

  81.Mann JK,Tager IB,Lurmann F,Segal M,Quesenberry CP Lugg MM,et al.

  Air pollution and Hospital Admissions for Ischemic Heart Disease in Persons with Congestive Heart Failure or Arrhythmia.Environmental Health Perspectives.2002;12:1247-52,doi:10.1289/ehp.021101247.

  82.Liao D,Duan Y,Whitsel EA,Zheng Z,Heiss G,Chinchilli VM,et al.

  Association of Higher Levels of Ambient Criteria pollutants with Impaired Cardiac Autonomic Control:A Population–based Study.

  Am J Epidemiol.2004;159;768-7.

  83.Pekkanen J,Brunner EJ,Anderson HR,Tiittanen P,Atkinson RW.Daily

  Concentrations of Air Pollution and Plasma Fibrinogen in London.

  Occup Environ Med.2000;57:818-22,doi:10.1136/oem.57.12.818.

  84.Elliot P,Shaddick G,Wakefield JC.Long term Associations of Outdoor

  Air Pollution with Mortality in Great Britain.Thorax.2007;62:1088-94, doi:10.1136/thx.2006.076851.

  85.Villeneuve PJ,Burnett RT,Shi Y,Krewski D,Goldberg MS,Hertzman

  C,et al.A Time Series Study of Air Pollution,Socioeconomic Status,and Mortality in Vancouver,Canada.J Exp Anal Environ Epidemiology.

  2003;13:427-5,doi:10.1038/sj.jea.7500292.

  86.Berglind N,Bellander T,Forastiere F,Klot S,Aalto P,Elosua R,et al.

  Ambient Air Pollution and Daily Mortality among Survivors of Myocardial Infarction.Epidemiology.2009;20:110-8,doi:10.1097/EDE.

  0b013e3181878b50.

  87.Liang WM,Wei HY,Kuo HW.Association Between daily Mortality from

  Respiratory and Cardiovascular Diseases and Air Pollution in Taiwain.

  Environ Research.2009;109:51-8,doi:10.1016/j.envres.2008.10.002. 88.Glorennec P,Monroux F.Health Impact Assessment of PM10Exposure

  in the City of Caen,France.J Toxicol Environ Health.2007;70:359-64, doi:10.1080/15287390600885039.

  89.Hoek G,Brunekreef B,Fisher P,Wijnen.The Association Between Air

  Pollution and Heart Failure,Arrhythmia,Embolism,Thrombosis,and Other Cardiovascular Causes of Death in a Time Series Study.

  Epidemiology.2001;12:355-7,doi:10.1097/00001648-200105000-00017.

  90.Oglesby LB,Grize L,Gassner M,Sahli KTS,Sennhauser FH,Neu U,

  et al.Decline of Ambient Air Pollution Levels and Improved Respiratory Health in Swiss Children.Environmental Health Perspectives.2005;113:1632-7,doi:10.1289/ehp.8159.

  91.Sekine K,Shima M,Nitta Y,Adachi M.Long Term Effects of Exposure

  to Automobile Exhaust on the Pulmonary Function of Female Adults in Tokyo,Japan.Occup Environ Med.2004;61:350-7,doi:10.1136/oem.

  2002.005934.

  92.Kim J J,Huen K,Adams S,Smorodinsky S,Hoats A,Malig B,et al.

  Residential Traffic and children’s Respiratory Health.Environmental Health Perspectives.2008;116:1274-9,doi:10.1289/ehp.10735.

  93.Kan H,Heiss G,Rose K,Witsel E,Lurmann F,London SJ.Traffic Exposure

  and Lung Function in Adults:The Atherosclerosis Risk in Communities Study.Thorax.2007;62:873-9,doi:10.1136/thx.2006.073015.

  94.Park SK,ONeill MS,Vokonas PS,Sparrow D,Wright RO,et al.Air

  Pollution and Heart Rate Variability.Epidemiology.2008;19:111-20, doi:10.1097/EDE.0b013e31815c408a.

  95.Sun R,Gu D.Air Pollution Economic Development of Communities,

  and Health Status among the Elderly in Urban China.Am J Epidemiol.

  2008;168:1311-8.

  96.Sunyer J,Jarvis D,Gotschi T,Esteban RG,Jacquemin B,Aguilera I,et al.

  Chronic Bronchitis and Urban Air Pollution in an International Study.

  Occup Environ Med.2006;63:836-43,doi:10.1136/oem.2006.027995.

  97.Brook R,Jerrett M,Brook J,Bard RL,Finkelstein MM.The Relationship

  Between Diabetes Mellitus and Traffic Related Air Pollution.J Occup Environ Med.2008;50:32-8,doi:10.1097/JOM.0b013e31815dba70.

  98.Martins LC,Latorre MRDO,Cardoso MRA,Gonc?alves LT,Saldiva PHN,

  Braga ALF.Air Pollution and emergency room visits due to Pneumonia and Influenza in Sa?o Paulo,Brazil.Rev Sau′de Pu′blica.2002;36;88-94. 99.Moura M,Junger WL,Mendonc?a GAS,Leon AP de.Air Quality and

  Acute Respiratory Disorders in Children.Rev Sau′de Pu′blica.2008;42:3. 100.Pereira Filho MA,Pereira LAA,Arbex FF,Arbex M,Conceic?a?o GM, Santos UP,et al.Effect of Air Pollution on diabetes and Cardiovascular Diseases in Sa?o Paulo,Brazil.Brazilian J Med Biolo Research.

  2008;41:526-32,doi:10.1590/S0100-879X2008005000020.

  101.Martins LC,Latorre MRDO,Saldiva PHN,Braga ALF.Air pollution and emergency Room Visits Due to Chronic Lower Respiratory diseases in the elderly:Na Ecological Time series Study in Sa?o Paulo,Brazil.J Occup Environ Med.2002;44:622-7,doi:10.1097/00043764-200207000-00006. 102.Cendon S,Pereira LAA,Braga ALF,Conceic?a?o GMS,Junior AC, Romaldini H,et al.Air Pollution Effects on Myocardial Infartion.Rev Sau′de Pu′blica.2006;40:414-9,doi:10.1590/S0034-89102006000300008. 103.Santos UP,Terra Filho M,Lin CA,Pereira LAA,Vieria TCB,Saldiva PHN,et al.Cardiac Arrhythmia Emergency Room Visits and Environmental Air Pollution in Sa?o Paulo,Brazil.J Epidemiol Community Health.2008;62:267-72,doi:10.1136/jech.2006.058123. 104.Farhat SCL,Paulo RLP,Shimoda TM,Conceic?a?o GMS,Lin CA,Braga ALF, et al.Effects of air Pollution on Pediatric Respiratory Emergency Room Visits and Hospital Admissions.Brazilian J Med Biol Research.2005;38:227-35. 105.Nascimento LF,Pereira LA,Braga ALF,Mo′dolo MCC,Carvalho Ju′nior JA.Effects of Air Pollution on Children’s Health in a city in Southeastern Brazil.Rev.Sau′de Pu′blica2006;40:1-5,doi:10.1590/ S0034-89102006000100013.

  106.Martins MCH,Fatigati FL,Ve′spoli TC,Martins LC,Pereira LAA, Martins MA,et al.Influence of Socioeconomic Conditions on Air pollution Adverse Health in Elderly People:An Analysis of Six regions in Sa?o Paulo,Brazil.J Epidemiol Community Health.2004;58:41-6,doi:

  10.1136/jech.58.1.41.

  107.Gouveia N,Fletcher T.Time Series Analysis of Air pollution and mortality:effects by Cause,Age and Socioeconomic Status.J.Epidemiol Health.2000;54:750-5,doi:10.1136/jech.54.10.750.

  108.Gouveia N,Freitas CU,Martins LC,Marcilio IO.Respiratory and Cardiovascular Hospitalizations Associated with Air Pollution in the City of Sa?o Paulo.Cad.Sau′de Pu′blica.2006;22:2669-77,doi:10.1590/ S0102-311X2006001200016.

  109.Gouveia N,Fletcher T.Repiratory Diseases in Children and Outdoor Air Pollution in Sa?o Paulo,Brazil:a Time Series Analysis.Occup Environ Med.2000;57:477-83,doi:10.1136/oem.57.7.477.

  110.Braga ALF,Pereira LAA,Proco′pio M,Andre PA,Saldiva PHN.Association Between Air Pollution and Respiratory and Cardiovascular diseases in Itabira,Minas Gerais State,Brazil.Cad.Sau′de Pu′blica.2007;4:S570-S578. 111.Lin CA,Pereira LAA,Nishioka,Conceic?a?o GMS,Braga ALF,Saldiva PHN.Air Pollution and Neonatal Deaths in Sa?o Paulo,Brazil.

  Brazil J Med Biol Research.2004;37:765-70.

  112.Bakonyi SMC,Oliveira IMD,Martins LC,Braga ALF.Air Pollution and Respiratory Diseases Among Children in Brazil.Rev Sau′de Pu′blica.

  2004;38:5,doi:10.1590/S0034-89102004000500012.

  113.Castro HA,Hacon S,Argento R,Junger WL,Mello CF de,Castiiglioni Ju′nior N,et al.Air Pollution and Respiratory Diseases in the Municipality of Vitoria,Esp?′rito Santo State,Brazil.Cad Sau′de Pu′blica.2007;23Sup4:S630-S642.

  114.Pereira LAA,Loomis D,Conceic?a?o GMS,Braga ALF,Arcas RM,Kishi HS,et al.Association Between Air pollution and Intrauterine Mortality in Sa?o Paulo,Brazil.Environ Health Perspectives.1998;106:325-9. 115.Martins LC,Pereira LAA,Lin CA,Santos UP,Prioli G,Luiz O do Carmo,et al.The effects of Air Pollution on Cardiovascular Diseases: Lag Structures.Rev Sau′de Pu′blica.32006;40:677-83.

  116.Lin CA,Martins MA,Farhat SCL,Pope III CA,Conceic?a?o GMS, Anastacio VM,et al.Air Pollution and Respiratory Illness of Children in Sa?o Paulo,Brazil.Paediatric and Perinatal Epidemiol.1999;13:475-488, doi:10.1046/j.1365-3016.1999.00210.x.

  117.Conceic?a?o GMS,Miraglia SGEK,Kishi HS,Saldiva PHN,Singer JM.Air pollution and Child Mortality:A Time Series Study in Sa?o Paulo,Brazil.

  Environ Health Perspectives.2001;109:347-50,doi:10.2307/3434781. 118.Junger WL,Leon AP.Air Pollution and Low Birth Weight in the City of Rio de Janeiro,Brazil,2002.Cad.Sau′de Pu′blica.2007;23Sup4:S588-S598. 119.Ribeiro H,Cardoso MRA.Air Pollution and Children’s Health in Sa?o Paulo(1986-1998).Social Science and Med.2003;57:2013-22,doi:10.

  1016/S0277-9536(03)00068-6.

  120.Rios JLM,Boechat JL,Sant’Anna CC,Sant’Anna CC,Franc?a ATF.

  Atmospheric Pollution and the Prevalence of Asthma:Study Among Schoolchildren of2Areas in Rio de Janeiro,Brazil.Ann Allergy Asthma Immunol.2004;92:629-34,doi:10.1016/S1081-1206(10)61428-7.

  CLINICS2011;66(4):681-690A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  121.Brilhante OM,Tambellini AMT.Particulate Suspended Matters and

  Cases of Respiratory Diseases in Rio de Janeiro City(Brazil).Int J Environ Health Research.2002;12:169-74,doi:10.1080/09603120220129337.

  122.Sobral H.Air Pollution and Respiratory Diseases in Children in Sa?o

  Paulo,Brazil.Soc Sci Med.1989;8:959-64,doi:10.1016/0277-9536(89)90051-8.123.Penna MLF,Duchiade MP.Contaminacio′n Del Aire y Mortalidad Infantil por Neumon?′a.Bol Sanit Panam.1991;110:199-207.

  124.Damaceno-RNRVeras MM,Negri EM,Zanchi AC,Rhoden CR,Saldiva PH,et al.Effect of pre-and postnatal exposure to urban air pollution on myocardial lipid peroxidation levels in adult mice.Inhal Toxicol.

  2009;2113:1129-37.

  A review of low-level air pollution and adverse effects on human health

  Olmo NRS et al.

  CLINICS2011;66(4):681-690

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  乐声:《西洋乐器》,轻工业出版社,1984年版 田进勤:《电子乐器》,人民邮电出版社,1984年版 H. K. 沃尔夫:《从晚期浪漫派到现代管弦乐法的发展概述》,载《近现代音乐研文集》,中国音乐家协会辽宁分会编,1985年版 朱起东:《圆号和它的特殊演奏法》,载《音乐艺术》 1985年第 2期 H. 伯夫:《圆号创新教学法》,人民音乐出版社,1987年版 施咏康:《管弦乐队乐器法》,人民音乐出版社,1987年版 人民音乐出版社编辑部编:《电子乐器译文集》,人民音乐出版社,1988年版 朱起东:《小号表演艺术》,上海音乐出版社,1992年版 丹尼斯. 维克:《长号吹奏技巧》,人民音乐出版社,1993年版 牟洪:《管弦乐队配器法》,人民音乐出版社,1999年版 三。其它 L . 坡林:《声音与意义-诗学概论》 罗曼. 罗兰:《现代音乐家评传》,上海群益出版社,1950年版 W . 辟斯顿:《和声学》,音乐出版社,1956年版 L . 玛采尔:《论旋律》,音乐出版社,1958年版 《乐记-乐本篇》,载《中国美学史资料汇编》,中华书局,1980年版 C. 波汶、B. 冯. 梅克编:《我的音乐生活》,人民音乐出版社,1982年版 P. H. 朗格:《十九世纪西方音乐文化史》,人民音乐出版社,1982年版 黛敏郎:《关于“涅磐”交响曲》,载中央音乐学院《外国音乐参考资料》,1983年第2-3期 F. 魏因迦特纳:《论贝多芬交响曲的演出》,人民音乐出版社,1984年版 Y. 秋林:《论音乐的写法》,人民音乐出版社,1984年版 陈铭志:《赋格曲写作》,上海音乐出版社,1980年版 I . 斯波索宾:《曲式学》,上海文艺出版社,1986年新二版

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  1. 中药材成分的影响。如有些中药材中含有大量的纤维成分。由于这些药材弹性大、黏性小,致使颗粒松散、片子硬度低。对此,在实际操作中可采用适宜的溶媒及方法,将此类药材中的有效成分提取浓缩,再进行颗粒制备,以降低颗粒弹性,提高可压性,进而提高片剂硬度;对含油脂量大的药材,压片亦易引起松片,如果这些油脂属有效成分,制粒时应加入适量吸收剂(如碳酸钙)等来吸油,如果这些油脂为无效成分,可用压榨法或其他脱脂法脱脂,减少颗粒油量,增加其内聚力,从而提高片子硬度。 2. 中药材粉碎度的影响。如果中药材细粉不够细,制成的颗粒黏结性不强,易使片剂松散。因此,药粉要具有一定细度,这是制好颗粒、压好药片的前提。 3. 黏合剂与湿润剂的影响。黏合剂与湿润剂在制粒中占有重要地位,其品种的选择和用量正确与否,都直接影响颗粒质量。选择黏合剂、湿润剂应视药粉性质而定,如是全生药粉压片,应选择黏性强的黏合剂,如是全浸膏压片,而浸膏粉中树脂黏液质成分较多,则必须选用80%以上浓度的乙醇作湿润剂。黏合剂用量太少,则颗粒细粉过多,会产生松片。 4. 颗粒中水分的影响。颗粒中的水分对片剂有很大影响,适量的水分能增加脆碎粒子的塑性变形,减少弹性,有利于压片,而过干的颗粒弹性大、塑性小,难以被压成片。但如果含水量太高,也会使药片松软,甚至黏冲或堵塞料斗,从而影响压片。故每一种中药片剂

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  ②黏合剂或润湿剂用量不足或选择不当,使颗粒质地疏松或颗粒粗细分布不匀,粗粒与细粒分层。可选用适当黏合剂或增加用量、改进制粒工艺、多搅拌软材、混均颗粒等方法加以克服。 ③颗粒含水量太少,过分干燥的颗粒具有较大的弹性、含有结 晶水的药物在颗粒干燥过程中失去较多的结晶水,使颗粒松脆,容易松裂片。故在制粒时,按不同品种应控制颗粒的含水量。如制成的颗粒太干时,可喷入适量稀乙醇(50汇60%,混匀后压片。 ④药物本身的性质。密度大压出的片剂虽有一定的硬度,但经 不起碰撞和震摇。如次硝酸铋片、苏打片等往往易产生松片现象;密度小,流动性差,可压性差,重新制粒。 ⑤颗粒的流动性差,填入模孔的颗粒不均匀。 ⑥有较大块或颗粒、碎片堵塞刮粒器及下料口,影响填充量。 ⑦压片机械的因素。压力过小,多冲压片机冲头长短不齐,车速过快或加料斗中颗粒时多时少。可调节压力、检查冲模是否配套完整、调整车速、勤加颗粒使料斗内保持一定的存量等方法克服。 2.裂片 片剂受到震动或经放置时,有从腰间裂开的称为腰裂;从顶部裂开的称为顶裂,腰裂和顶裂总称为裂片,原因分析及解决方法: ①药物本身弹性较强、纤维性药物或因含油类成分较多。可加入糖粉以减少纤维弹性,加强黏合作用或增加油类药物的吸收剂,充分混匀后压片。 ②黏合剂或润湿剂不当或用量不够,颗粒在压片时粘着力差。

  管弦乐队音乐-弦乐组基础理论与MIDI音序法实战教程——上 Read me

  管弦乐配器法与MIDI制作,似乎向来是高等音乐学府里面的神秘知识,一般不为喜欢音乐的朋友们所了解,而写出并且制作出一段大气的好莱坞式的管弦乐或者影视配乐,一直是朋友们心目中的梦想。然而,市场上关于管弦乐MIDI制作与配器的教材是非常少的,而且不成体系,实用性不强。出于这一考虑,我们制作并编写了这套《管弦乐配器法与MIDI制作教程》以献给朋友们。 本教程的内容是非常具有体系性的,是音乐学院教授们的研究成果,可供音乐学院学生,专业音乐人士和业余音乐爱好者们学习使用或作参考。本教程从最基本的管弦乐队基本原理讲解起,针对每一种乐器进行完整的专题的讲解,并且从旋律的配器,和声织体的配器以及综合配器角度讲解乐器组的配器手法和MIDI音序法(即MIDI制作),为了更好地讲解音乐,讲解配器手法,本教程在宿主软件Overture内演示,其既能显示五线谱,管弦总谱,又能进入钢琴卷帘窗口进行MIDI修饰,还能加载VST插件等。 我们尽量在短的教程内融入更多的知识与经验,并加入实际的例子进行实战讲解,使朋友们既能学习到完整的配器理论,又能与MIDI 制作联系起来,使自己能够学着制作管弦乐。同时也希望朋友们循序渐进,要知道管弦乐配器不是一朝一夕可以学得透彻的,必须一步一个脚印,相信时间不久的将来一定会有惊喜的收获。 本教程的体系是这样的:弦乐组配器基础理论与实战教程,木管组配器基础理论与实战教程,铜管组配器基础理论与实战教程,打击乐与综合配器基础理论与实战教程。

  本系列教程所选的例子均为音乐学院教授精心挑选的例子,很能说明管弦乐配器课题,希望朋友们能引起重视。 本教程全称名为《管弦乐队弦乐组基础理论与MIDI音序法实战教程——上》,时长约2小时10分钟,分为两个大部分,介绍如下:(1)管弦乐队基本理论:该部分最为重要,是所有管弦乐队配器的基础,其涉及到一系列的基本原理,都适用 到以后的配器法的学习中,并且在学习一段时间之后 再回顾会有不小的启发。该部分讲解了管弦乐队组织 的基本原理,各种乐器介绍,乐器组介绍,乐队概念 介绍,以及重要的乐队音响的六个表现要素理论:音 质与音色,音区,密度,厚度,声部排列,力度。 (2)弦乐组基本理论与MIDI音序法实战:该部分进入到弦乐组的配器学习中,并且结合MIDI处理讲解配器 法,因此相比较一般的配器教程更有针对性。首先介 绍发音原理,其次介绍重要的定弦,音域与音区问题, 接着是各种乐器音色的讲解,结合以不同的典型例子 讲解旋律与音色的关系。接下来是把位介绍和最重要 的弓法理论与MIDI音序法:连弓弓法与MIDI音序法, 断弓弓法与MIDI音序法,震音弓法与MIDI音序法, 每种弓法都有实际的例子讲解应用。接下来是和弦和 双音理论,这在配器中也是很常用的,能取得较好效 果。接下来是特殊演奏技法:拨弦理论与MIDI音序

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