THE THE URBAN ATMOSPHERE URBAN ATMOSPHERE OF THE OF THE 21 21 ST ST CENTURY CENTURY
Dec 10, 2015
THETHE URBAN ATMOSPHERE URBAN ATMOSPHERE OF THEOF THE 21 21STST CENTURY CENTURY
INHERITANCE FROM 20INHERITANCE FROM 20THTH CENTURYCENTURY
Liquid fuel – secondary pollution – photochemistry – inversion
Yet traditional problems such as odour remain
POPs
WOOD SMOKE VOCs, O3
COAL SMOKE DIESEL SMOKE
LEAD H2SSMELLs
TIME
DOMINANCE of the DOMINANCE of the AUTOMOBILEAUTOMOBILE
2OPHOTOCHEMICALPOLLUTION
CARCINOGENS
NEUROTOXINENDOCRINE DISRUPTOR
TERATOGEN
OK EXCEPT OK EXCEPT FOR 2FOR 2NDND POLLUTIONPOLLUTION
EPA ambient air quality
trends
UK: QUALITY OF URBAN AIR UK: QUALITY OF URBAN AIR REVIEW GROUP (QUARG)REVIEW GROUP (QUARG)
Review groups and their context Networks and public
communication Preparation for EC directives
SMOG OF 1991SMOG OF 1991
12th to the 15th of December 1991 estimated that smog caused around
160 more deaths than normal Cardiovascular (up 14%) and
respiratory (up 22%) deaths increased Schwartz and Dockery
QUARG and OUTPUTQUARG and OUTPUT
Reports focus on particulate matter (especially PM10 and PM2.5 and diesel
KUZNETS CURVEKUZNETS CURVE
The environmental Kuznets curve relationship between indicators of environmental degradation
income per capita
Simon Kuznets' hypothesis- as a country develops, Simon Kuznets' hypothesis- as a country develops, there is a natural cycle of economic inequality driven there is a natural cycle of economic inequality driven by market forces which at first increases inequality, by market forces which at first increases inequality, and then decreases and then decreases
KUZNETS RELATIONSHIPKUZNETS RELATIONSHIP
Inverted U-shape curves of pollutants over time seen as economically driven
Pollutant concentrations in London follow a Kuznets curve
Such curves particularly evident for pollutants creating localised problems that offer local benefits via regulation. INCOME PER CAPITA
INEQUALITY
INDUSTRIALIZATION
POLLUTION
BRIMBLECOMBE & GROSSI Millennium-long damage to building materials in London, Science of the Total Environment 407, 1354 (2009).
NZNZ RESOURCE MANAGEMENT REGULATIONSRESOURCE MANAGEMENT REGULATIONS
Regulations of 2004 as allowed under Resource Management Act 1991 (RMA)
Note it is about management and quote Elsom on Air Quality Management Clean Air and Environmental Quality, Volume 38, 1.
(2004)
http://www.mfe.govt.nz/publications/rma/user-guide-draft-oct05/html/page3.html
NZNZ RESOURCE MANAGEMENT REGULATIONSRESOURCE MANAGEMENT REGULATIONS
Regional council plans determine paths to comply with the fine particle standard by 1 September 2013
http://www.mfe.govt.nz/publications/rma/user-guide-draft-oct05/html/page3.html
REGULATION OF PMREGULATION OF PM
Confusion over mechanisms and measurement
regulation of size not effects
Regulatory problems: uncertainty no-thresholds
Constitutional dilemmasTSP PM10 PM2.5
0
2.5
5
7.5
10
PM10 PM2.5
Dia
me
ter/
mic
ron
s
PROBLEMS WITH STANDARDSPROBLEMS WITH STANDARDS
Meeting limit values may not always reduce exposure most effectively
CONCENTRATIONCONCENTRATION
LIMITLIMITVALUEVALUE
Fails to meet limitFails to meet limitvalue, but much reducedvalue, but much reducedcumulative doescumulative does
CURRENTCURRENT
Meets limitMeets limitvaluevalue
PREVENTION OF SIGNIFICANT PREVENTION OF SIGNIFICANT DETRIMENT (PSD): embodied in CAA(1977)DETRIMENT (PSD): embodied in CAA(1977)
Sierra Club challenged EPA approval that allowed air quality degradation in areas having air quality better than the national ambient air quality standards.
Sierra Club v. Ruckelshaus (1972)
Giant Forest in Sequoia National Park http://www.nps.gov/archive/seki/snrm/air/visibility.htm
$$$$PARIS $$$$PARIS OZONE AND OZONE AND HEATWAVE HEATWAVE 20032003
Smog’n Paris (& 400 000 morts prématurées en Europe, chaque année)
Climate change and increasing ozone?
OZONEOZONE TREND TREND
Daily max 8 hour ozone Bridge Place London then Westminster – μg/m3
0
20
40
60
80
100
120
140
160
180
200
90.00 92.00 94.00 96.00 98.00 100.00 102.00 104.00 106.00 108.00 110.001990 2000 2008
0
10
20
30
40
50
60
1100 1300 1500 1700 1900 2100
Longer term issues – temperature and sunlight may increase ozone, but precursors may decline
INTERGRATED EXPOSURE TO INTERGRATED EXPOSURE TO SUMMER OZONESUMMER OZONE
AOT40 for forests in England (Harwell, Aston Hill and Ladybower)
April-September daytime ozone over threshold of 40 ppb
AIR POLLUTION AND AIR POLLUTION AND FREEDOMSFREEDOMS Mode of transport
– congestion charges
Regulation of indoor spaces and furnishings
Bonfires in gardens
HOPLEY, E. BRIMBLECOMBE, P. Clean Air & Env Prot. 32, 75-77 (2002)
THE SCHOOL RUN
POLLUTION & POLLUTION & PLEASUREPLEASURESUVs and 2-STROKESSUVs and 2-STROKES
Diesel soot 2-stroke particles -
condensed heavy hydrocarbons
Lawn-mowers contribute 5-12% CO/HC in Australian cities.
FIREWORKSFIREWORKS
Celebrations a complex issue for policy makers…
Nov 5th PM10 LONDON
1800 2400 0600
MILLENNIUM EDINBURGH
DOMESTIC /CULTURAL EMISSIONSDOMESTIC /CULTURAL EMISSIONS
Domestic indoor heating and cooking Wood and coal
Cultural outdoor burning Hangi Umu
Bonfires
Image source: Te ara Encyclopedia of New Zealand www.teara.govt.nz/EarthSeaAndSky/ClimateAndAtmosphere/Atmosphere/5/ENZ-Resources/Standard/2/2/
en#breadcrumbtop
NES does not regulate domestic fires
Plan includes rules for domestic fires, but regulation difficult
AGGRESSIVE AGGRESSIVE APPROACHESAPPROACHES
Mayor Ken Livingstone Legal challenges Congestion or pollution
control Profitability Transfer to other cities
CONGESTION CHARGINGCONGESTION CHARGING London from Feb 2003London from Feb 2003
12% reduction in NO2
15% reduction in vehicle km Expected increase from buses have been
offset by introduction of particle traps Reduction in NOX and PM10 from increases
in vehicle speed (~ 2.1 km h-1) Early lack of acceptance may have been
thwartedBeevers and Carslaw (2005a,b)
SECONDARY ORGANIC AEROSOLSECONDARY ORGANIC AEROSOL Recognising that the organic
material formed in the smog was important
Oxidized compounds, but necessarily non volatile – e.g. dicarboxylic acids
0
20
40
60
80
100
120
140
160
180
400 800 1200 1600 2000
hours
NO2
NO
O3
HC
RCHO
TRANSFORMATION ON PARTICLESTRANSFORMATION ON PARTICLES
PAH lifetime on wood smoke and gasoline soot
aldehyde of 5a,b-secobenzo(a)pyrene
2.2 min 200 min 5.7 days
anthanthrene pyrenebenzo(a)pyrene
ON SILICA ON SILICA SURFACESSURFACES
OXIDATION OF NAPTHALENEOXIDATION OF NAPTHALENE
hν, SiO2
OH, NO
SOLUBILIZATION OF NAPTHALENESOLUBILIZATION OF NAPTHALENE
0
5
10
15
0 2 4 6
Surfactant mMol/l
Kh
mo
l/l.
atm
K = mC10H8/pC10H8
Mario Massucci UEA
Surfactants in alveoli aid gas exchange, but also lung defence.
Would aerosol surfactants alter these functions?
PULMONARY SURFACTANTSPULMONARY SURFACTANTS
PULMONARY SURFACTANTS
ALVEOLIALVEOLI
0
10
20
30
40
50
Hydrocarbon CO NOx
gra
m/m
ile
gasoline
CNG
LPG
ALTERNATE ALTERNATE FUELSFUELS
g/mile H/C CO NOx
gasoline 3.1 42 6.2
CNG 0.5 8.6 2.1
LPG 0.45 1.0 1.1
Data gathered in the late 1980s…
METHANOLMETHANOL IMPACT IN A IMPACT IN A LARGE CITYLARGE CITY
Peak 1h ozone little change
Average O3 improves PAN reduced Increased peak HCHO,
but average does not change much
BIOFUELSBIOFUELS
Methanol –expensive to produce from biomass Ethanol - from sugar cane
automotive fuel in Brazil. Ethanol corn derived gasoline additive in the US, from cellulose waste, perhaps for NZ forest
products industry Biodiesel - Rudolf Diesel’s engine designed for
peanut oil Direct use of bagasse, rice husks
BIOFUELS - PROBLEMSBIOFUELS - PROBLEMS
Wasteful as it often comes from food crops such as corn, sugar, soya oil…
Methanol leads it high formaldehyde concentrations
Methanol/ethanol very water soluble Biodiesel may lead to high NOx emissions Bagasse, rice husks or wood
may have high hydrochloric acid emissions
http://www.ens-newswire.com/ens/jan2002/2002-01-04-06.asp