9.4. Other Chemically Active Gases
The SRES emissions scenarios also have different emissions for other GHGs and
chemically active species such as CO, NOx , and volatile organic compounds.
The uncertainties that surround the emissions sources of these gases, and the
more complex set of driving forces behind them are considerable and unresolved.
Hence, model projections of these gases are particularly uncertain and the scenarios
presented here are no exception. Improved inventories and studies linking driving
forces to changing emissions in order to improve the representation of these
gases in global and regional emission models remain an important future research
task.
The emissions of other gases follow dynamic patterns much like those shown
in Figure TS-7 for carbon dioxide emissions. Further details about GHG emissions
are given in Chapter 5.
9.4.1. Nitrogen Oxides Emissions
Some models of the six SRES models do not provide a comprehensive description
of NOx emissions or include only specific sectors (e.g., energy-related sources)
and have adopted other source categories from corresponding model runs derived
from other models. Even with a simplified model representation, future NOx emission
levels are mainly determined by two set of variables: levels of fossil energy
use (see Chapter 4), and level and timing of emission
controls, inspired by local air quality concerns.
As a result the spread of NOx emissions is largest within the A1 scenario family
(28 to 151 MtN/yr by 2100), almost as large as the range across all 40 SRES
scenarios (see Table TS-4). Only in the highest
emission scenarios (the fossil fuel intensive scenarios within the A1 scenario
family and the high population, coal intensive A2 scenario family) do emissions
rise continuously throughout the 21st century. In the A1B ("balanced") scenario
group and in the B2 scenario family, NOx emission levels rise less. NOx emissions
tend to increase up to 2050 and stabilize thereafter, the result of a gradual
substitution of fossil fuels by alternatives as well as of the increasing diffusion
of NOx control technologies. Low emission futures are described by various B1
family scenarios, as well as in the A1T scenario group, that describe futures
in which NOx emissions are controlled because of either local air quality concerns
or rapid technological change away from conventional fossil technologies. Overall,
the SRES scenarios describe a similar upper range of NOx emissions as the previous
IS92 scenarios (151 MtN versus 134 MtN, respectively, by 2100), but extend the
IS92 uncertainty range toward lower emission levels (16 versus 54 MtN by 2100
in the SRES and IS92 scenarios, respectively).
9.4.2. Volatile Organic Compounds, Excluding Methane
NMVOCs arise from fossil fuel combustion (as with NOx , wide ranges of emission
factors are typical for internal combustion engines), and also from industrial
processes, fuel storage (fugitive emissions), use of solvents (e.g., in paint
and cleaners), and a variety of other activities. In this report NMVOCs are
discussed as one group. As for NOx emissions, not all models include the NMVOCs
emissions category or all of its sources.
A relatively robust trend across all 40 scenarios (see Chapter 5) is a gradual
increase in NMVOC emissions up to about 2050, with a range between 190 and 260
Mt. Beyond 2050, uncertainties increase with respect to both emission levels
and trends. By 2100, the range is between 58 and 552 Mt, which extends the IS92
scenario range of 136 to 403 Mt by 2100 toward both higher and lower emissions
(see Table TS-4). As for NOx emissions, the upper
bounds of NMVOC emissions are formed by the fossil fuel intensive scenarios
within the A1 scenario family, and the lower bounds by the scenarios within
the B1 scenario family. Characteristic ranges are between 60 and 90 Mt NMVOC
by 2100 in the low emissions cluster and between 370 and 550 Mt NMVOC in the
high emissions cluster. All other scenario families and individual scenarios
fall between these two emissions clusters; the B2 marker scenario (B2-MESSAGE)
closely tracks the median of global NMVOC emissions from all the SRES scenarios
(see Chapter 5).
9.4.3. Carbon Monoxide Emissions
The same caveats as stated above for NOx and NMVOC emissions also apply to
CO emissions - the number of models that represent all the emission source categories
is limited and modeling and data uncertainties, such as emission factors, are
considerable. As a result, CO emission estimates across scenarios are highly
model specific and future emission levels overlap considerably between the four
SRES scenario families (see Table TS-4). Generally,
emissions are highest in the high growth fossil fuel intensive scenarios within
the A1 scenario family. Lowest emission levels are generally associated with
the B1 and B2 scenario families. By 2100, emissions range between 363 and 3766
Mt CO, a considerably larger uncertainty range, particularly toward higher emissions,
than in IS92, for which the 2100 emission range was between 450 and 929 Mt CO
(see Table TS-4).
9.5. Emissions Overview
Table TS-4 (see later) summarizes the emissions
of GHGs, sulfur dioxide and other radiatively active species by 2100 for the
four markers and the ranges for other 36 scenarios. Combined with Tables TS-2
and TS-3, the tables provide a concise summary
of the new SRES scenarios. Data are given for both the harmonized and all scenarios.
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