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Aerosols and the pause

There is a new commentary piece in Nature Geoscience by Gavin Schmidt and colleagues on ‘Reconciling warming trends’. The paper investigates several potential causes for the discrepancy between climate model projections and the recent ‘slowdown’ in global surface temperatures, which is nicely illustrated on Ed Hawkins’ Climate Lab Book blog.

One of the aspects the paper looks at is the influence of aerosol particles in the troposphere (the lower part of the atmosphere), which tend to exert a cooling influence on our climate. Of the aspects they looked at, aerosol particles are the most uncertain.

As I summarised in this previous post, the final report from the Intergovernmental Panel on Climate Change (IPCC) on the physical science basis concluded that aerosols was continue to dominate the uncertainty in the human influence on climate. They said that a complete understanding of past and future climate change requires a thorough assessment of aerosol-cloud-radiation interactions.

With this in mind, I want to delve into the details of how the chemical make-up of aerosol particles varies across the globe and how this is important for our climate and how this relates to the warming trends paper.

What are aerosols made of?

Aerosols are made up of a large variety of different chemical species, which vary by the time of day, seasonally, regionally and a host of other factors. There is no single type of aerosol in our atmosphere.

The figure below attempts to pull together a huge collection of studies that have been measuring the major aerosol chemical species in different regions of the globe. We can see on the map that many of the sites are in North America and Western Europe, where large coordinated surface networks have been making such measurements for decades. Measurements elsewhere are much more limited, particularly in the Southern Hemisphere.

This is one of the major difficulties in understanding aerosols; they are difficult to measure, the techniques used are typically quite labour intensive and they require access to well developed infrastructure and supporting measurements.

Fig7.13-Final-2

Summary of aerosol chemical species split across different regions based on surface measurements. The map shows the locations of the sites. For each area, the panels represent the median, the 25th to 75th percentiles (box), and the 10th to 90th percentiles (whiskers) for each aerosol component. The colour code for the measured components is shown in the key where SO4 refers to sulphate, OC is organic aerosol (strictly organic carbon), NO3 is nitrate, NH4 is ammonium, EC is black carbon (strictly elemental carbon), mineral refers to mineral dust e.g. from deserts and sea-salt refers to aerosols produced by ocean waves. The figure is 7.13 from the IPCC report, where the numerous references for the data are included. Click on the image for a larger view. Source: IPCC.

Bearing this in mind, we are able to draw some broad conclusions on their chemical make-up. We can see that in all of the non-marine regions, the aerosol is broadly made up of sulphate, organic carbon, nitrate, ammonium and black carbon, with the influence of mineral dust varying depending on location e.g. concentrations are much greater in locations such as Africa and Asia where large deserts exist.

Of these species, sulphate, nitrate, ammonium and black carbon are predominantly man-made in origin, while organic carbon can be a consequence of both natural and man-made emissions. We see that concentrations of organic carbon and nitrate are broadly equivalent to those of sulphate, with organic carbon being much greater in South America, Oceania, Africa and parts of Asia.

Where is the aerosol?

One of the key properties of aerosol particles in the troposphere is that they have a short lifetime, as they are removed from the atmosphere by rain or simply by crashing into things (terrible drivers those aerosol particles). This typically means that the largest concentrations occur near their sources; they are regionally very important in a climate context but their impact evens out at larger scales, although they do still exert a global influence.

Below is an illustration of this based on satellite measurements combined with a forecast model system, which shows ‘hotspots’ of aerosol particles over China, India and Southern Africa in particular. The metric used here is the aerosol optical depth, which is a measure of the amount of aerosol present in a vertical slice through the atmosphere.

Horizontal and vertical distributions of aerosol amount based on a combination of the European Centre for Medium Range Weather Forecasts (ECMWF) Integrated Forecast System model with satellite measurements from the Moderate Resolution Imaging Spectrometer (MODIS) averaged over the period 2003–2010 and the Cloud–Aerosol Lidar with Orthogonal Polarization (CALIOP) instrument for the year 2010. The figure is 7.14 in the IPCC report and references for studies are available there. Click on the image for a larger view. Source: IPCC.

Comparing the two figures, we see that the enhanced aerosol optical depth in Asia is consistent with the large aerosol concentrations measured by the surface based networks. Of the man-made species, organic carbon is a big driver here, with nitrate, sulphate and ammonium also playing a major role. These aerosol particles are formed due to the substantial emissions from the region.

What about the pause?

Of these species, sulphate and black carbon are the major species that climate models have historically focussed on. Organic carbon is generally included, although there are large discrepancies in relation to measurements, particularly related to the secondary organic aerosol component. Nitrate has received comparatively little attention and those that have included it have shown that it is an important aerosol species both today and over the 21st Century. Drew Shindell and colleagues when comparing aerosol optical depth from satellite measurements and climate models concluded that:

A portion of the negative bias in many models is due to missing nitrate and secondary organic aerosol.

I’ve been involved in research showing how nitrate is important in North-Western Europe and how it enhances the aerosol radiative forcing in the region (many others have done so also by the way). Nitrate has long been known to be important in North America, particularly in California, where large urban and agricultural emissions coincide. Several studies have investigated its importance in East Asia, showing that it is particularly prevalent during the winter.

The ‘Reconciling warming trends’ commentary notes that nitrate was only included in two of the models that contributed to the Coupled Model Intercomparison Project (CMIP5) and that including this across all models brings them closer to the observed surface temperature trend. They also note that underestimating the secondary organic aerosol contribution would have a similar effect but don’t put a value on this.

While this certainly isn’t the last word on the importance of these species for climate change and research on the ‘pause’ will undoubtedly continue, further recognition of their contribution to atmospheric aerosol is a step in the right direction. There are many unanswered questions in this realm, particularly relating to the large differences across climate models in terms of what contribution each species makes to regional and global aerosol.

Bringing the aerosol measurement and modelling communities together more to address such issues is likely the way forward. This is a big focus in many aerosol related research projects these days…we’re trying, honest.

Fires in South East Asia

Smoke from a number of agricultural fires is currently blanketing Thailand and Cambodia. This is shown below in the satellite image from the MODIS instrument on the TERRA satellite. The red dots are classed as ‘thermal anomalies’ by the satellite instrument and are usually indicative of fires burning in these locations.

The majority of the fires are occurring in grass and cropland areas, which are the bale brown portions of the land surface in the image. This is indicative of agricultural burning, where farmers clear land and use the fires to recycle nutrients ahead of the growing season. In South-East Asia, the fire season usually runs from January to April/May.

Image of fires in South East Asia and the associated smoke haze from 24th February 2014 from the Moderate Resolution Imaging Spectroradiometer (MODIS) instrument on the TERRA satellite. Image courtesy of the NASA Earth Observatory. Click on the image for a larger view.

While the burning is beneficial to farmers, it isn’t too good for air quality in the region. The smoke generated by the fires has built up over Cambodia and Thailand (contrast the clearness of the image in the top-left over Myanmar with the haze to the east). The MODIS instrument on the satellite can also measure the amount of pollution in the atmosphere. This is known as the aerosol optical depth, which is well above 0.5 across the region. For context, a fairly polluted day in North-Western Europe might seen an aerosol optical depth of around 0.2.

This build up of pollution is harmful to health and can also cool or warm the atmosphere depending on the properties of the smoke. The side affects of such changes are uncertain but they could for instance alter atmospheric circulation patterns and rainfall.

Fires are a frequent occurrence across the globe and their impact can have long lasting consequences on our health and climate.

AGU 2013 roundup

Now that the 2013 AGU Fall Meeting has ended, I thought I would roundup what I’ve been involved with over the week for both this blog and the Barometer Podcast, which I was recording each day with Sam Illingworth. Links to each piece are available below. Many thanks to all who have read and shared these over the past week.

Recording the podcast at conferences is becoming a trend as we’ve covered AGU now in 2012 and 2013 plus the EGU in 2013. Recording these is a lot of fun and particular thanks should go to Dave ToppingBethan Davies and Mark Brandon for giving up their time to chat to us this week. Lastly, many thanks to Sam for his infectious enthusiasm and for being the only person I’ve ever met with a louder laugh than me.

The conference itself was excellent throughout, even if the amount of science on offer was overwhelming at times. The sessions on science communication I attended were also fantastic, thought-provoking and often inspiring. I’m planning to write a separate post on this aspect over the coming days.

So long San Francisco! Image: Will Morgan

So long AGU 2013 and thanks for all the science! Image: Will Morgan

Blog posts

Podcasts

http://thebarometer.podbean.com/2013/12/10/fires-beer-and-satellites-day-1-at-agu/

http://thebarometer.podbean.com/2013/12/10/disappointment-aerosols-and-methane-burps-day-2-at-agu/

http://thebarometer.podbean.com/2013/12/12/hansen-nuclear-power-and-geologists-day-3-at-agu/

http://thebarometer.podbean.com/2013/12/13/science-communication-viscosity-and-londons-greenhouse-gases-day-4-at-agu/

http://thebarometer.podbean.com/2013/12/13/communicating-big-data-and-a-love-of-models-day-5-at-agu/

AGU 2013 day 1: Short-lived climate forcers

My first day at AGU 2013 revolved around sessions on short-live climate forcers, which are components in the atmosphere that have short lifetimes (compared to carbon dioxide for example) and generally warm the atmosphere. Reduction of these compounds, such as methane and black carbon, has been mooted as a way to reduce global mean temperatures in coming decades.

This is summarised in the figure below, where the modelled impact of reducing black carbon and methane alongside reductions in carbon dioxide emissions are shown. The majority of the benefit in reducing methane and black carbon is felt by 2040 – if you look at longer time scales, then the effect diminishes relative to carbon dioxide.

image

Modelled impact of various reductions in carbon dioxide, methane and black carbon (BC) on global mean temperature. Figure courtesy of UNEP Integrated Assessment of Black Carbon and Tropospheric Ozone.

The problem with this idea is that there is much uncertainty related to these short-lived components, so it isn’t clear how much global temperatures would respond to a reduction in their atmospheric concentrations. This is represented in the above figure by the vertical bars to the left of the graph – there is much overlap here, which reflects this uncertainty. The health benefits of reducing black carbon in particular are quite clear though. Most of the talks focussed on black carbon and that is what I am also going to focus on below.

Fuzzy metrics

Tami Bond made some excellent and thought-provoking points on how short-lived climate forcers are framed relative to carbon dioxide. The key property for black carbon in the framework of near-term reductions in global temperature is its short lifetime in the atmosphere (days-to-weeks). This means that it is not evenly distributed across the globe, unlike greenhouse gases such as carbon dioxide and methane. This results in its radiative forcing being spatially distinct – the perturbation it has on our planets energy balance occurs close to its source of emission. The impact of such changes is usually felt more at the regional level, rather than the global scale associated with carbon dioxide. Her main point was that this is then an apples-to-oranges comparison, so for example, reducing black carbon emissions in Asia might not have a great impact of global mean surface temperatures but it may well reduce temperatures in the region and slow the effects of carbon dioxide driven warming.

She also reiterated the difficulties associated with the pollutants that are co-emitted with black carbon, which complicate the picture and are one of the major reasons that there is substantial uncertainty surrounding reducing black carbon. In the real world, you can’t really just reduce black carbon – any technological  solution will likely perturb the other pollutants, which tend to cool our climate. Attempts to reduce black carbon might actually result in temperatures rising – I’ve written more on studies that have considered this here.

Other highlights

Yi Deng presented a fascinating study of how aerosol particles can influence the atmosphere far away from their actual location by modelling the impact of biomass burning in Southern Africa on the Asian Summer Monsoon. He showed that the substantial burning that occurs actually strengthens the monsoon by inducing circulation changes up-wind of the Indian sub-continent and south-east Asia. We tend to think of aerosol impacts being confined to their atmospheric location but this illustrated how joined-up our atmosphere is.

One of the issues with black carbon is that some sources have received little attention previously. Ed Fortner from Aerodyne Research Inc. presented measurements of emissions from brick kilns in Mexico, which produce a lot of black carbon. There are around 300,000 kilns worldwide producing 1.5 billion bricks per year! Over half of these are in China (54%), with India (11%), Pakistan (8%) and Mexico (7%)  being the other major kiln hotspots. Characterising the emissions from these and other sources is likely going to be in important for efforts to constrain the impact of black carbon on both our climate and health.

Chris Cappa presented follow-up work to his 2012 paper in Science that investigated how much warming by black carbon is enhanced by other aerosol species that coat it. Black carbon warms the atmosphere by absorbing sunlight and both laboratory and theoretical evidence suggests that this is increased by coatings on the black carbon particles. This coating focusses sunlight onto the black carbon core, like a magnifying glass held to the sun does and this increases the absorption by the black carbon, a phenomenon known as “lensing”. Chris has been busy testing how much enhancement we see in the real world using measurements and typically to enhancement ranges from 10-30%, which is lower than is often suggested by aerosol models. There are significant caveats here as the measurements are challenging and require the aerosols to be “dry” – this is important as water often condenses onto aerosol particles and increases their reflective and lensing ability. This could be a vital ingredient in this process and it is a significant challenge to overcome.

My final highlight was presenting my poster! The AGU poster hall is absolutely massive and must span several football pitches. Despite this, the sessions are hugely rewarding and are a great opportunity to discuss science with a variety of people. The posters are a major part of the AGU fall meeting, which is not always true of other conferences. I’m looking forward to roaming the hall now that my own poster is done.

Me presenting my poster on day 1 of AGU 2013. Image courtesy of Sam Illingworth.

Me presenting my poster on day 1 of AGU 2013. Image courtesy of Sam Illingworth.

Communicating uncertainty

With all this complexity revolving around black carbon and the interest it has received from policy makers, Tami Bond was asked how to communicate this to non-scientists. Her response was:

Keep it simple but don’t ignore physical reality.

That seems like a pretty good mantra to me.