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Since the introduction of CO2 laser surgery, surgeons have stressed the importance of protecting
nontarget structures from errant irradiation. Although striking areas outside the intended field
may inflict little or no damage, irradiating an exposed endotracheal tube may result in an
endotracheal fire. Recent experience with a case of endotracheal tube ignition led to reevaluation
of those factors associated with this serious complication. In an attempt to determine the best
endotracheal tube to use during laser surgery of the larynx, the flammability of polyvinyl
chloride and red rubber endotracheal tubes was compared. Several factors were noted to
contribute to the potential hazard of endotracheal tube ignition. Since red rubber tubes are less
flammable, they should be used during laryngeal CO2 laser surgery. Present data on the total
amount of CO2 in the atmosphere, on the rates and mechanisms of exchange, and on possible
fluctuations in terrestrial and marine organic carbon, are inadequate for accurate measurement of
future changes in atmospheric CO2. An opportunity exists during the International Geophysical
Year to obtain much of the necessary information. Emissions of carbon dioxide from the
combustion of fossil fuels, which may contribute to long-term climate change, are projected
through 2050 using reduced-form models estimated with national-level panel data for the period
of 1950–1990. Using the same set of income and population growth assumptions as the
Intergovernmental Panel on Climate Change (IPCC), we find that the IPCC's widely used
emissions growth projections exhibit significant and substantial departures from the implications
of historical experience. Our model employs a flexible form for income effects, along with fixed
time and country effects, and we handle forecast uncertainty explicitly. We find clear evidence of
an “inverse U” relation with a within-sample peak between carbon dioxide emissions (and
energy use) per capita and per-capita income. Analyses of ecosystem responses to global change
must embrace the reality of multiple, interacting environmental factors. Ecosystem models
demonstrate the importance of examining the combined effects of the gradually rising
concentration of atmospheric CO2 and the climatic change that attends it. Models to forecast
future changes need data support to be useful, and data–model fusion has become essential in
global change research. There is a wealth of information on plant responses to CO2 and
temperature, but there have been few ecosystem-scale experiments investigating the combined or
interactive effects of CO2 enrichment and warming. Factorial experiments to investigate
interactions can be difficult to design, conduct, and interpret, and their results may not support
predictions at the ecosystem scale – in the context of global change they will always be case
studies. An alternative approach is to gain a thorough understanding of the modes of action of
single factors, and rely on our understanding (as represented in models) to inform us of the
probable interactions. Multifactor (CO2 × temperature) experiments remain important, however,
for testing concepts, demonstrating the reality of multiple-factor influences, and reminding us
that surprises can be expected. Terrestrial ecosystems are constantly responding to an ever
fluctuating variety of biotic and abiotic influences. Daily and seasonal changes in light,
temperature and humidity are obvious features of any natural environment, and they define the
distribution of species and biomes. Ecosystems persist (usually) through drought years and wet
years, unusually cool and unusually warm years. Insects and disease can alter the structure of
ecosystems, sometimes with predictable regularity but often with no warning. Superimposed on
this complex suite of influences are the gradually rising concentration of CO2 in the atmosphere
and the climatic change that attends it. Sorting out the myriad natural influences from those
caused by human activities is an extraordinary challenge.
Increasing atmospheric CO2 concentration and rising average global temperature are well
documented changes in the global environment, and their origin in human activity is clear (IPCC,
2001a). Understanding how ecosystems respond to simultaneous increases in atmospheric CO2
and temperature, and how they will respond in the future, is imperative. „The ecosystems of the
world are critical foundations of human society‟ (Committee on Global Change Research, 1999).
Ecosystems deliver goods and services to humankind that are critical for our survival – food,
materials, energy, water and less tangible qualities. Maintaining the flow of those goods and
services requires maintaining healthy ecosystems in the face of human-caused changes in the
global environment. Furthermore, ecosystems play key roles in regulating the cycling of carbon
(C) and the flow of energy, and hence they participate in the shaping of weather, climate,
atmospheric composition and climate change.

Forecasting how rising CO2 and temperature will affect ecosystems in the future has been the
subject of many modeling exercises over a wide range of detail and sophistication. Most early
efforts considered only one factor at a time, leading to seemingly incompatible conclusions: „The
projected climatic changes will destroy forests over large areas‟ (Woodwell, 1986) and „In fact,
if the air's CO2 content were ever to double or triple, the productivity of the planet's trees may
possibly rise severalfold‟ (Idso & Kimball, 1993). Clearly, ecosystems will not experience global
warming without the co-occurrence of elevated CO2, and how they respond will be a function of
the combined effects of CO2 and temperature. As recognized in the third assessment report of the
IPCC (2001b), it is no longer useful to examine the impacts of climate change without including
their interactions with rising atmospheric CO2. Hence, both CO2 and temperature effects were
incorporated into the projections that were conducted as part of the comprehensive National
Assessment of Climate Change Impacts on the United States (Melillo et al., 2001), as well as in
retrospective analyses of global vegetation responses to climatic change since the last glacial
maximum (Harrison & Prentice, 2003). These efforts have illustrated the importance of including
CO2 fertilization effects in estimating responses to both past and future climate change, despite
the uncertainty in the magnitude of the response.

The predictions of future responses depend on how the effects of rising temperature and CO2 are
represented in the models, and the three models used in the National Assessment differ in some
of their assumptions (Table 1). Several questions arise: Are the representations of CO2 and
temperature effects in the models reasonable and in agreement with what is known from direct
observations and experimentation? Do the results of experiments in which CO2 and temperature
are manipulated agree with model projections (and is this a reasonable question)? Do
experiments inform us about interactions between CO2 and temperature that are missing from
models?

The effects of elevated CO2 have been investigated in many experiments with different species
and over a range of scales from the chloroplast to the ecosystem. Most of these have been single-
factor experiments; other environmental variables (e.g. temperature, soil moisture, N availability)
were either constant (as in a growth chamber experiment) or uncontrolled. Some insights into
CO2 × temperature interaction might be gleaned from analysing the responses to CO2 in relation
to diurnal or seasonal variation in temperature (Naumburg et al., 2004), but temperature variation
will inevitably be confounded by other plant and environment factors. Air temperature is more
difficult to manipulate than CO2 in experiments outside of growth cabinets, and there have been
far fewer ecosystem-scale experiments (Rustad et al., 2001). Many warming experiments have
elevated only soil temperatures (using buried heating cables) or primarily canopy temperatures
(using infrared heaters), making interpretation of results difficult (Rustad et al., 2001). Whole-
ecosystem warming experiments have been conducted in grasslands (Luo et al., 2001a; Saleska
et al., 2002), but existing technologies (and financial resources) essentially preclude similar
experiments in intact forests. Hence, available data on forest responses come from soil warming
experiments (Melillo et al., 2002; Stromgren & Linder, 2002), treatment of individual trees
(Peltola et al., 2002), small assemblages of young trees (Norby et al., 2000; Olszyk et al., 2003;
Turnbull et al., 2004), or unreplicated enclosures over intact ecosystems (Wright, 1998). It is not
surprising, then, that despite the wealth of information on plant responses to the interaction of
CO2 and temperature (Morison & Lawlor, 1999), there have been few ecosystem-scale
experiments investigating the combined or interactive effects of CO2 enrichment and warming.

Factorial experiments can be difficult to implement. Inevitable limitations on the number of
experimental units, due to financial constraints or space availability, often require a trade-off
between the number of treatments and the number of replications. The number of different
treatment combinations and possible outcomes often leads to vague hypotheses and confusing
results. With limited replication there is often insufficient statistical power to detect interactions,
defeating the primary purpose of conducting factorial experiments. (By „interaction‟ we mean
the situation in which the direction or magnitude of the response to one variable depends on the
value of one or more other variables; in this case, the combined effect of the two variables is not
simply the sum of the responses to the two variables alone.) It might well be more efficient to
gain a thorough understanding of the modes of action of single factors, and rely on our
understanding (as represented in models) to inform us of the probable interactions. Before we
adopt such a strategy, we should explore the benefits and pitfalls of CO2 × temperature factorial
experiments.

Product Features

        200 bar operation
        Integral supercritical fluid compressor
        Ambient temperature to 773 K operation
        Enhanced anti-condensation protection
        Versatile instrument control
        Multi-gas control providing programmable sorbate selection

Product Applications

        Isotherm determination
        Carbons
        Zeolites
        Ionic liquids
        Metal-Organic Frameworks (MOFs)
        Isosteric enthalpy of adsorption determination
        Energy gas storage
        Carbon Capture and Storage (CCS)
Shale gas and Coal Bed Methane (CBM)
Geological carbon dioxide sequestration

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Since the introduction of co2

  • 1. Since the introduction of CO2 laser surgery, surgeons have stressed the importance of protecting nontarget structures from errant irradiation. Although striking areas outside the intended field may inflict little or no damage, irradiating an exposed endotracheal tube may result in an endotracheal fire. Recent experience with a case of endotracheal tube ignition led to reevaluation of those factors associated with this serious complication. In an attempt to determine the best endotracheal tube to use during laser surgery of the larynx, the flammability of polyvinyl chloride and red rubber endotracheal tubes was compared. Several factors were noted to contribute to the potential hazard of endotracheal tube ignition. Since red rubber tubes are less flammable, they should be used during laryngeal CO2 laser surgery. Present data on the total amount of CO2 in the atmosphere, on the rates and mechanisms of exchange, and on possible fluctuations in terrestrial and marine organic carbon, are inadequate for accurate measurement of future changes in atmospheric CO2. An opportunity exists during the International Geophysical Year to obtain much of the necessary information. Emissions of carbon dioxide from the combustion of fossil fuels, which may contribute to long-term climate change, are projected through 2050 using reduced-form models estimated with national-level panel data for the period of 1950–1990. Using the same set of income and population growth assumptions as the Intergovernmental Panel on Climate Change (IPCC), we find that the IPCC's widely used emissions growth projections exhibit significant and substantial departures from the implications of historical experience. Our model employs a flexible form for income effects, along with fixed time and country effects, and we handle forecast uncertainty explicitly. We find clear evidence of an “inverse U” relation with a within-sample peak between carbon dioxide emissions (and energy use) per capita and per-capita income. Analyses of ecosystem responses to global change must embrace the reality of multiple, interacting environmental factors. Ecosystem models demonstrate the importance of examining the combined effects of the gradually rising concentration of atmospheric CO2 and the climatic change that attends it. Models to forecast future changes need data support to be useful, and data–model fusion has become essential in global change research. There is a wealth of information on plant responses to CO2 and temperature, but there have been few ecosystem-scale experiments investigating the combined or interactive effects of CO2 enrichment and warming. Factorial experiments to investigate interactions can be difficult to design, conduct, and interpret, and their results may not support predictions at the ecosystem scale – in the context of global change they will always be case studies. An alternative approach is to gain a thorough understanding of the modes of action of single factors, and rely on our understanding (as represented in models) to inform us of the probable interactions. Multifactor (CO2 × temperature) experiments remain important, however, for testing concepts, demonstrating the reality of multiple-factor influences, and reminding us that surprises can be expected. Terrestrial ecosystems are constantly responding to an ever fluctuating variety of biotic and abiotic influences. Daily and seasonal changes in light, temperature and humidity are obvious features of any natural environment, and they define the distribution of species and biomes. Ecosystems persist (usually) through drought years and wet years, unusually cool and unusually warm years. Insects and disease can alter the structure of ecosystems, sometimes with predictable regularity but often with no warning. Superimposed on this complex suite of influences are the gradually rising concentration of CO2 in the atmosphere and the climatic change that attends it. Sorting out the myriad natural influences from those caused by human activities is an extraordinary challenge.
  • 2. Increasing atmospheric CO2 concentration and rising average global temperature are well documented changes in the global environment, and their origin in human activity is clear (IPCC, 2001a). Understanding how ecosystems respond to simultaneous increases in atmospheric CO2 and temperature, and how they will respond in the future, is imperative. „The ecosystems of the world are critical foundations of human society‟ (Committee on Global Change Research, 1999). Ecosystems deliver goods and services to humankind that are critical for our survival – food, materials, energy, water and less tangible qualities. Maintaining the flow of those goods and services requires maintaining healthy ecosystems in the face of human-caused changes in the global environment. Furthermore, ecosystems play key roles in regulating the cycling of carbon (C) and the flow of energy, and hence they participate in the shaping of weather, climate, atmospheric composition and climate change. Forecasting how rising CO2 and temperature will affect ecosystems in the future has been the subject of many modeling exercises over a wide range of detail and sophistication. Most early efforts considered only one factor at a time, leading to seemingly incompatible conclusions: „The projected climatic changes will destroy forests over large areas‟ (Woodwell, 1986) and „In fact, if the air's CO2 content were ever to double or triple, the productivity of the planet's trees may possibly rise severalfold‟ (Idso & Kimball, 1993). Clearly, ecosystems will not experience global warming without the co-occurrence of elevated CO2, and how they respond will be a function of the combined effects of CO2 and temperature. As recognized in the third assessment report of the IPCC (2001b), it is no longer useful to examine the impacts of climate change without including their interactions with rising atmospheric CO2. Hence, both CO2 and temperature effects were incorporated into the projections that were conducted as part of the comprehensive National Assessment of Climate Change Impacts on the United States (Melillo et al., 2001), as well as in retrospective analyses of global vegetation responses to climatic change since the last glacial maximum (Harrison & Prentice, 2003). These efforts have illustrated the importance of including CO2 fertilization effects in estimating responses to both past and future climate change, despite the uncertainty in the magnitude of the response. The predictions of future responses depend on how the effects of rising temperature and CO2 are represented in the models, and the three models used in the National Assessment differ in some of their assumptions (Table 1). Several questions arise: Are the representations of CO2 and temperature effects in the models reasonable and in agreement with what is known from direct observations and experimentation? Do the results of experiments in which CO2 and temperature are manipulated agree with model projections (and is this a reasonable question)? Do experiments inform us about interactions between CO2 and temperature that are missing from models? The effects of elevated CO2 have been investigated in many experiments with different species and over a range of scales from the chloroplast to the ecosystem. Most of these have been single- factor experiments; other environmental variables (e.g. temperature, soil moisture, N availability) were either constant (as in a growth chamber experiment) or uncontrolled. Some insights into CO2 × temperature interaction might be gleaned from analysing the responses to CO2 in relation to diurnal or seasonal variation in temperature (Naumburg et al., 2004), but temperature variation will inevitably be confounded by other plant and environment factors. Air temperature is more difficult to manipulate than CO2 in experiments outside of growth cabinets, and there have been
  • 3. far fewer ecosystem-scale experiments (Rustad et al., 2001). Many warming experiments have elevated only soil temperatures (using buried heating cables) or primarily canopy temperatures (using infrared heaters), making interpretation of results difficult (Rustad et al., 2001). Whole- ecosystem warming experiments have been conducted in grasslands (Luo et al., 2001a; Saleska et al., 2002), but existing technologies (and financial resources) essentially preclude similar experiments in intact forests. Hence, available data on forest responses come from soil warming experiments (Melillo et al., 2002; Stromgren & Linder, 2002), treatment of individual trees (Peltola et al., 2002), small assemblages of young trees (Norby et al., 2000; Olszyk et al., 2003; Turnbull et al., 2004), or unreplicated enclosures over intact ecosystems (Wright, 1998). It is not surprising, then, that despite the wealth of information on plant responses to the interaction of CO2 and temperature (Morison & Lawlor, 1999), there have been few ecosystem-scale experiments investigating the combined or interactive effects of CO2 enrichment and warming. Factorial experiments can be difficult to implement. Inevitable limitations on the number of experimental units, due to financial constraints or space availability, often require a trade-off between the number of treatments and the number of replications. The number of different treatment combinations and possible outcomes often leads to vague hypotheses and confusing results. With limited replication there is often insufficient statistical power to detect interactions, defeating the primary purpose of conducting factorial experiments. (By „interaction‟ we mean the situation in which the direction or magnitude of the response to one variable depends on the value of one or more other variables; in this case, the combined effect of the two variables is not simply the sum of the responses to the two variables alone.) It might well be more efficient to gain a thorough understanding of the modes of action of single factors, and rely on our understanding (as represented in models) to inform us of the probable interactions. Before we adopt such a strategy, we should explore the benefits and pitfalls of CO2 × temperature factorial experiments. Product Features 200 bar operation Integral supercritical fluid compressor Ambient temperature to 773 K operation Enhanced anti-condensation protection Versatile instrument control Multi-gas control providing programmable sorbate selection Product Applications Isotherm determination Carbons Zeolites Ionic liquids Metal-Organic Frameworks (MOFs) Isosteric enthalpy of adsorption determination Energy gas storage Carbon Capture and Storage (CCS)
  • 4. Shale gas and Coal Bed Methane (CBM) Geological carbon dioxide sequestration