For instance, Figure 20 compares the average monthly pressure of the phase change to the average monthly
ozone concentrations for the 45 - 60 ° N band.
When we compared the seasonal variations in
ozone concentrations for each band to the seasonal variations in the phase change conditions, we found they were both highly correlated!
Not exact matches
Those who were exposed to the highest
concentrations of
ozone were about 20 percent more likely to develop diabetes, even after adjusting
for other possible explanations such as diet and exercise levels.
So Weschler and Wisthaler simulated a typical office environment at the Technical University of Denmark in Copenhagen — two people in a carpeted 28.5 — cubic meter room at a temperature of 23 degrees Celsius with two small stainless steel tables, two chairs, two flat - screen LCD monitors, two headsets, one walkie - talkie, one small mixing fan, a few books, two laptops, two bottles of water and
ozone concentrations that reached roughly 32 parts per billion, an average exposure
for a hot, smoggy day.
8 hour average
ozone concentrations of 85 to 104 ppbv are described as «Unhealthy
for Sensitive Groups», 105 ppbv to 124 ppbv as «unhealthy» and 125 ppb to 404 ppb as «very unhealthy.»
Although the Montreal Protocol came into force in 1987 and restricted the use of
ozone - depleting substances, atmospheric
concentrations of these harmful substances continued to rise as they can survive in the atmosphere
for many years.
NASA's upper atmosphere research satellite,
for example, carries the British - made microwave limb sounder (MLS) which measures
concentrations of chlorine monoxide — a chemical that plays a critical part in the destruction of
ozone.
Even though open windows bring in more
ozone from outside, the reduction in the indoor limonene
concentration and SOA formation strength more than make up
for it, as less secondary organic aerosol is formed inside.
High
ozone concentrations typically occur outside of the cities and represent a risk factor
for the health of rural population as well as
for agricultural production.
For O3, the design value represents the three - year average of the fourth highest daily 8 - hour maximum
ozone concentration.
The specialized instruments onboard the aircraft sampled the plume
for aerosol particle size distribution and composition as well as
concentrations of pollutant gases such as sulfur dioxide, nitric oxide, nitrogen dioxide,
ozone, and volatile organic compounds (VOCs).
This assumes that ambient
ozone concentrations measured at the monitor location are representative of population exposure (see e.g. Meng et al. 2012; US EPA 2013
for a discussion of the validity of this assumption).
Pallas is one of the sites of the Finnish network
for monitoring the
concentrations of mercury and other heavy metals, benzo (a) pyrene,
ozone and other air pollutants, as required by the European legislation on ambient air quality.
The Pallas research infrastructure has been extensively instrumented
for modern and versatile monitoring of the environment since the start of continuous monitoring of atmospheric sulphur dioxide (SO2) and
ozone (O3)
concentrations at Sammaltunturi in September 1991, and with the setup of the Global Atmosphere Watch (GAW) station in 1994.
• increases in malnutrition and consequent disorders, with implications
for child growth and development; • increased deaths, disease and injury due to heat waves, floods, storms, fires and droughts; • the increased burden of diarrheal disease; • the increased frequency of cardio - respiratory diseases due to higher
concentrations of ground - level
ozone related to climate change; and, • the altered spatial distribution of some infectious disease vectors.
Of course, though some of the flux up at the tropopause escapes directly to space, and some is absorbed by CO2 (over the whole stratosphere in the wings of the CO2 band, concentrated towards the base of the stratosphere
for larger optical thicknesses), some is absorbed by
ozone (with variable
concentration), and some by water vapor.
Scientists use the word hole as a metaphor
for the area in which
ozone concentrations drop below the historical threshold of 220 Dobson Units.
In 1991, a new threshold was passed;
ozone concentration fell below 100 DU
for the first time.
Although
concentrations should level off as the Montreal Protocol on Substances which Deplete the
Ozone Layer is implemented, CFCs have long life - times, and their effects will be felt
for many decades to come.
Pallas is one of the sites of the Finnish network
for monitoring the
concentrations of mercury and other heavy metals, benzo (a) pyrene,
ozone and other air pollutants, as required by the European legislation on ambient air quality.
Due to the important role of
ozone in driving temperature changes in the stratosphere as well as radiative forcing of surface climate, several different groups have provided databases characterizing the time - varying
concentrations of this key gas that can be used to force global climate change simulations (particularly
for those models that do not calculate
ozone from photochemical principles).
Debates over the optimal level of
ozone have been ongoing
for many years, and current efforts to strengthen environmental regulations affecting
ozone concentrations remain contentious.
Icelandic volcanoes are about 30 degrees away from the pole, too far except
for the strongest eruptions, to be swept - up (in suficient enough
concentration) into the stratosphere by polar vortex, hence the
ozone layer there is more stable, despite fact there was more CFC around in the Nth than Sth hemisphere.
This study of course does not take away very different concerns related to stratospheric aerosol SRM geoengineering, like possible damage to the
ozone layer [which in turn would be good news if you hate waiting
for that spring tan] and the fact that allowing CO2
concentrations to keep rising presents other problems, like the necessity to never stop with the active process of SRM geoengineering, and increasing ecological damage caused by ocean acidification.
During extreme heat events, nighttime temperatures in the region's big cities are generally several degrees higher28 than surrounding regions, leading to increased heat - related death among those less able to recover from the heat of the day.36 Since the hottest days in the Northeast are often associated with high
concentrations of ground - level
ozone and other pollutants, 37 the combination of heat stress and poor air quality can pose a major health risk to vulnerable groups: young children, the elderly, and those with pre-existing health conditions including asthma.29 Vulnerability is further increased as key infrastructure, including electricity
for potentially life - saving air conditioning, is more likely to fail precisely when it is most needed — when demand exceeds available supply.
Pace the phrase «any air pollutant,» everything in § 115 points to it being meant to apply only to NAAQS pollutants, i.e., those
for which EPA has established a «National Ambient Air Quality Standard»: a numerical value representing the appropriate atmospheric
concentration of
ozone, particulate matter, etc..
It is the primary pathway
for global - scale equator - pole transport in the stratosphere and has implications
for ozone concentrations.
Langmann, B., and S.E. Bauer, 2002: On the importance of reliable background
concentrations of
ozone for regional scale photochemical modelling.
Your preference
for the CFC explanation instead is bizarre because you have no idea of the scale of the effect of the positive AO on
ozone concentrations.
Other researchers used historical (real - world) data
for land use, atmospheric CO2
concentration, nitrogen deposition, fertilization,
ozone levels, rainfall and climate, to develop a computer model that simulates plant growth responses
for southern US habitats from 1895 to 2007.
The caveat is that these molecules can weakly absorb sunlight in the near IR and visible on combination and overtone bands, mostly of water vapor, and on weakly absorbing forbidden transitions such as the Chappius bands of
ozone, and
for very low
concentrations of dimers.
Atmospheric
concentrations of LLGHGs have increased (see Chapter 2) and are expected to continue to increase, with consequences
for the
ozone layer.
Not surprisingly, highly populated regions such as the Los Angeles, Riverside and Houston areas, where the climate is sunny
for much of the year and the air mass is relatively stable, had the highest average
concentrations of
ozone, ranging from 62.5 to 104 ppb.
High
ozone levels downstream of pollution sources can cause elevated OH radical
concentrations, which in turn increases the
concentration of condensable species and thus the potential
for nucleation.
Since a large body of evidence links pollution with poor health, and health is an important part of human capital, efforts to reduce pollution could plausibly be viewed as an investment in human capital and thus a tool
for promoting economic growth... We find robust evidence that
ozone levels well below federal air quality standards have a significant impact on productivity: a 10 ppb decrease in
ozone concentrations increases worker productivity by 4.2 percent.
We present an analysis of how three alternative scenarios
for US power plant carbon standards could change fine particulate matter and
ozone concentrations in ambient air, and the resulting public health co-benefits.