CO2 Impacts Tropical Forest Resistance to Climate Change

by Leta Ames

It is well known that fire can play a crucial role in the reproduction and development of plant populations. The availability of water and CO2 also impact plant growth, especially of larger species. It is believed that the interactions of climate, fire, and CO2 greatly influence the shift between savanna and tropical forest ecosystems and their permanence thereafter. Previous research has relied on data collected from intact tropical forests, but although useful, these data only provide a snapshot of the impact of CO2, fire, and climate on these ecosystems. To gain a better understanding of what factors influence tropical ecosystems Shanahan et al. (2016) used the concentrations of carbon and hydrogen stable isotopes from sedimentary leaf wax n-alkanes (δ13Cwax and δDwax) and the frequency of charcoal layers from sediment obtained from Lake Bosumtwi in Ghana to construct a history of changes in vegetation and hydrology, as well as to estimate the annual fire frequency. Continue reading

Anthropogenic effects on greenhouse gas (CH4 and N2O) emissions in the Guadalete River Estuary (SW Spain)

by Rebecca Herrera

Burgos et al. (2014) discuss seasonal variations of the greenhouse gases methane (CH4) and nitrous oxide (N2O) in the Guadalete River Estuary ending in the Cadiz Bay of southwestern Spain. They found that greenhouse gas concentrations were higher in the more inland parts of the estuary compared to the mouth of the river. Concentrations of methane and nitrous oxide varied depending largely upon the seasonal precipitation regime. It was also observed that the Guadalete Estuary acted as a source, rather than a sink, of greenhouse gases throughout the entire year, as observed by measuring the fluxes of CH4 and N2O from the Estuary. Continue reading

Heat Stress and Low Humidity with Climate Change will be Hard on Midwestern Corn Crops


by Christina Whalen and Emil Morhardt

Maize (corn) production continues to be a very important source of food, feed, and fuel all around the world, but climate change has raised the concern about being able to maintain the yield rates. A negative relationship between extremely high temperatures (above 30˚C) and yield has already been observed in various regions. Previous studies have not been able to demonstrate which mechanism causes the correlation between extreme temperatures and yield, thus it is possible that the relationship reflects the influence of another variable, such as precipitation rates. There are other possible explanations for the observed relationships. This study explores the mechanisms used in other studies that document the importance of extreme heat on rainfed maize using the process-based Agricultural Production Systems Simulator (APSIM). The study asks three main questions: can APSIM reproduce the empirical relationships—what farmers are seeing on the ground?; if so, what does APSIM imply are the key processes that give rise to these relationships?; how much are these relationships affected by changes in atmospheric CO2? Continue reading

Elevated CO2 Affects Tropical Marine Fish Predator-Prey Interactions

by Jennifer Fields

Recent research has demonstrated that exposure to elevated CO2 affects how fish observe their environment, affecting behavioral and cognitive processes leading to increased prey mortality. However, it is unknown if increased prey mortality is caused by changes in kinematics of predator-prey interactions or from just increasing prey activity levels. Allan et al. (2013) studied the effect of anticipated end of this century CO2 concentrations on the predatory-prey interaction of two tropical marine fish. Both a predator and prey fish was exposed to present day and elevated CO2 levels in a cross-factored design. The authors investigated the changes in locomotion performance, prey reaction distance, and capture success of the interaction. Authors found that predators Continue reading

Species Most Vulnerable to Climate Change

by Elizabeth Medford

While it has been recognized in the past that climate change will have impacts on biodiversity, many approaches ignore the differences between species that will increase or reduce their vulnerability. Foden et al. (2013) chose to address three different aspects of climate change vulnerability to account for species’ biological traits: sensitivity, exposure, and adaptive capacity. In combining these traits with the modeled exposure to projected climate change, the authors assessed the species with the greatest relative vulnerability to climate change. These methods were applied to each of the world’s birds, amphibians, and corals. The authors also identified the geographic areas in which the most vulnerable species are concentrated. These included the Amazon basin for amphibians and birds, and the Indo-west Pacific for corals. The aim of Foden et al. is that Continue reading

A Review of CO2 Enrichment Studies: Does Enhanced Photosynthesis Enhance Growth?

Plants typically only convert 2 to 4% of available energy into actual growth and this natural inefficiency provides a reason for scientists to attempt to increase the efficiency of the process by increasing photosynthesis. One of the most common methods, other than genetic modification, to increase photosynthesis is to increase ambient CO2. Elevated CO2 can lead to growth increases ranging from 10 to 50%, depending on the plant’s carbon sink capacity and nutrient availability. Previous studies show that elevated CO2inevitably leads to increased growth, but the magnitude of the growth varies with the photosynthetic capacity of the plant. Photosynthesis is an inefficient process with a maximum of 8 to 10% of the energy in sunlight being converted into chemical energy. Realistically, only 2 to 4% of energy in sunlight is converted. In this paper, Kirschbaum examines previous studies and conducts experiments of his own in order to summarize the current knowledge on CO2enrichment studies, focusing on the ability of increased photosynthesis to ultimately increase plant growth. Kirschbaum studies the factors that affect plant growth under elevated CO2 in an attempt to determine if photosynthesis is the main factor increasing growth or if other factors are relatively more important.—Taylor Jones
Kirschbaum, M.U.F., 2011. Does Enhanced Photosynthesis Enhance Growth? Lessons Learned from CO2 Enrichment Studies.  Plant Physiology 155, 117-124.

          Kirschbaum first examines the photosynthetic response to increasing CO2concentrations and distinguishes between Rubisco-limited photosynthetic rates and ribose 1,5-bisphosphate (RuBP) regeneration-limited rates. For both photosynthetic rates, the relative responsiveness of increases in CO2concentration decreases as atmospheric CO2 continues to increase. Photosynthesis is limited by Rubisco-limited rates at low CO2concentrations and RuBP regeneration-limited rates at high concentrations, and scientists argue that the amounts of Rubisco plants have today is in excess of what is needed, so most plants experience RuBP regeneration-limited photosynthesis. Changes in plant photosynthesis are supported by previous studies, as 30 to 40% enhancements in photosynthesis were recently found in free-air CO2 enrichment experiments and a 58% increase was found in a controlled plot experiment. Kirschbaum notes that there are important limitations to any photosynthesis study as plants that experience less light and increased self-shading may have less enhancement of photosynthesis, while plants grown in high temperature conditions may have more. On average, increases in ambient CO2 lead to a 30% enhancement of photosynthesis, but does this translate to a 30% enhancement of growth?
          Studies show that the relative growth rate for plants is often similar among species and enhanced photosynthesis often leads to only a 10% increase in the relative growth rate. Kirschbaum suggests that previous studies show an increases in photosynthesis leads to 20% enhanced leaf area, but also a 6.5% increase in leaf weight due to increase amounts of carbohydrates and this leads to an ineffective transformation of increased photosynthetic rates to new growth. Extra amounts of carbon produced from photosynthesis can only be of use if the plant can utilize it through root growth, new foliage, or other carbon sinks. Also, carbon cannot be used efficiently if other vital resources, such as nitrogen, are lacking. Studies have shown that many plants show strong photosynthetic enhancement during the growth stages, reduced enhancement during the flowering stages and then increased enhancement during the fruiting stages. During the flowering stages, plants lost much of their potential carbon sink that exists in the growth phase and is regained through seed production in the flowering stage. Most plants show some increased growth response to elevated CO2, but the degree of this growth is determined by other limiting factors, such as carbon sink and nitrogen availability.
          Kirschbaum also notes that a large number of papers use biomass enhancement ratios to determine the effects of elevated CO2 on plant growth. Biomass enhancement ratios are often much greater than relative growth rates and also greater for single-plant studies and fast-growing plants. Under elevated CO2, plants often experience exponential growth in early stages, followed by average growth rates in intermediate stages. Plants that experience an overall relative growth rate of 10% can experience a biomass enhancement ratio of 50% in intermediate stages which eventually decreases to about 10% in later stages. This concept explains why fast-growing plants can have higher biomass enhancement ratios compared to slower-growing plants, but the same relative growth rate. Therefore, the length of an experiment is very important and should be considered when examining the biomass enhancement ratio of a plant to determine if real growth increases exist. The biomass enhancement ratio can often be a misleading value as it can be manipulated by varying the length of an experiment.
          Kirschbaum identifies other issues that may affect photosynthetic enhancement rates that need to be considered, such as natural competition and growth response in mixed-species communities. Also, some studies have shown a decrease in protein concentrations under elevated CO2. Plant herbivore interactions might also change as elevated CO2 usually leads to lower nutrient concentrations which reduces the rate of herbivores feeding on the plant and as a result, herbivores may attempt to consume more of the plant. All of these factors are important complicating issues and should be addressed further.
          In conclusion, photosynthetic enhancement due to elevated CO2 increases the carbon available to plants and whether or not this translates to growth depends on other colimiting factors, such as nutrient availability and carbon sink. Increases in carbon will exacerbate any other limitations. Plants are also subjected to genetic constraints and will only respond to increases in photosynthesis to levels within their genetic capability. By examining several CO2 enrichment experiments, Kirschbaum found that growth enhancements are modest and a 10% increase in relative growth rate can translate to a much higher relative growth rate in the early exponential phases of plant growth. Kirschbaum suggests that genetic manipulation of photosynthesis should include appropriate crop management and close examination of plant attributes to maximize photosynthetic enhancement.

The Effects of Increased CO2 on Biomass and Exogenous-Toxin Quantity in Transgenic Bt Cotton and Rice Crops

Transgenic crops have become an increasingly important component of modern agroecosystems, ideally providing environmentally friendly, disease resistant crops with combinations of multiple genes that improve productivity and agricultural yield. One of the most common types of transgenic crop is Bacillus thuringiensis (“Bt”), which is produced worldwide and exhibits a strong resistance to lepidopteran pests in multiple cropping environments. With CO2 levels expected to increase in the future, scientists question the ability of Bt crops to adapt to changing atmospheric conditions and some hypothesize that increasing CO2 will pose new ecological risks for Bt crops and possibly reduce their effectiveness against target pests. In this study, a series of open-top chamber (OTC) experiments were conducted to asses whether measured exogenous-toxin quantity is reduced in transgenic Bt cotton and rice due to increased plant biomass under elevated atmospheric CO2. This study also examines the effectiveness of Bt cotton and rice transgenes against H. armigera and C. suppressalislarvae respectively. The study showed that there are significant differences between the exogenous-toxin levels of Bt cotton and rice under increased CO2and both showed differences in toxin quantity among developmental stages. Also, the new properties of Bt crops under elevated CO2 significantly affected the performance of H. armigeraand C. suppressalis larvae, despite the adverse effects of Bt gene expression in elevated CO2conditions.—Taylor Jones
Chen, F., Wu, G., Ge, F., Parajulee, M. N., 2011. Relationships between exogenous-toxin quantity and increased biomass of transgenic Bt crops under elevated carbon dioxide. Ecotoxicology and Environmental Safety 74, 1074–1080.

          Chen and colleagues performed a series of OTC experiments with ambient (375μl/L) and elevated (750μl/L) CO2  conditions that were maintained via a continuous automatic control system. Thirty-six pots of transgenic Bt cotton and twenty-six pots of transgenic Bt rice were planted and their positions were randomized each day to limit positional effects in the OTC chambers. In select plots, cotton bollworm (H. armigera) and rice stem borer C. suppressaliswere added to examine the effects of pest larvae on Bt cotton and rice. Biomass index was used to determine the increased amount of biomass under elevated CO2conditions and plant tissues were tested for exogenous-toxin quantity. Chen et al. recognize the potential “dilution effect” in which percent biomass increase exceeds the percent increase in exogenous-toxin increase, resulting in decreased levels of exogenous-toxin.
          The results show that increasing CO2levels significantly increased leaf, petiole, shoot and total plant biomass production of 45-DAS (“days after seedling”) Bt cotton as well as increases in shoot and total plant biomass production in 90-DAS cotton. Similar trends resulted for Bt rice as root, above-ground, and total stem biomass increased in 50-DAS rice and root tissues increased in 100-DAS rice. Overall, elevated levels of CO2 led to increased biomass in Bt cotton and rice, as predicted by previous studies showing increased photosynthesis and growth rates.
          Elevated CO2 conditions significantly reduced exogenous-toxin content in both Bt cotton and rice tissues. However, the effect of CO2 level on exogenous-toxin amount varied among crops and their respective plant tissues. For example, increased CO2 significantly reduced exogenous-toxin content per plant in 45-DAS and 90-DAS Bt cotton, while simultaneously increasing exogenous-toxin content in the stems of 50-DAS Bt rice. This shows that the responses of transgenic Bt cotton and rice (relating to exogenous-toxin content) to increased ambient CO2 are different. Also, each plant exhibited different responses in different phases of development. Chen and colleagues compared percent changes in biomass and exogenous-toxin levels and concluded that a dilution effect exists in shoot and petiole tissues of 45-DAS Bt cotton and in root, above-ground, and total stem tissues of 50-DAS Bt rice as well as leaf sheaths of 100-DAS rice. This is probably related to increased plant nitrogen-use efficiency and the authors predict that increased plant carbohydrate concentration diluted Bt proteins. For other increases in exogenous-toxin levels, the authors conclude that the dilution effect is only partly responsible and the reduction is due to reduced expression of the Bt gene under increased CO2 conditions.
          The results also suggest that most H. armigera larvae preferred to feed on transgenic Bt cotton squares and bolls, and most C. suppressalis larvae preferred to feed upon leaf sheaths of transgenic Bt rice. These areas of the Bt crops correlate with decreases in exogenous-toxin production, as expected. Although feeding increased in certain areas, the study found overall decreases in larval survival rate and pupal weight of H. armigera and C. suppressalis, suggesting that the Bt cotton and rice in this study to not face serious risks of reduced efficiency against pests in increased CO2 conditions.

Estimated Magnitude of Persistent Carbon Sink in World’s Forests

Forests are important in absorbing a significant amount of CO2 in the earth’s atmosphere. It is necessary to understand how much of an effect they have in order to set limitations on greenhouse gas emissions and better understand the effects of climate change. The Intergovernmental Panel on Climate Change (IPCC) reports a wide range of data on the C uptake by terrestrial ecosystems, stating that uptake could range from less than 1.0 to 2.6 Pg per year. More recent models on climate change report a C sink range of 2.0 to 3.4 Pg per year. Understanding and constraining these limitations is crucial in understanding the future effects of climate change. In this report, the authors carried out a bottom-up estimation of C stocks and changes based on recent data and long-term field observations coupled with statistical modeling. The C pools in forest include measurements from dead wood, harvested wood, living biomass, litter, and soil. Data from different countries, regions, and continents was compared to understand trends across geographic boundaries. The area examined contains 3.9 billion ha, which accounts for 95% of the world’s forests. —Taylor Jones
Pan, Y., Birdsey, R. A., Fang, J., Houghton, R., Kauppi, P. E., Kurz, W. A., Phillips, O. L., Shvidenko, A., Lewis, S. L., Canadell, J. G., Ciais, P., Jackson, R. B., Pacala, S. W., McGuire, A. D., Piao, S., Rautiainen, A., Sitch, S., Hayes, D., 2011. A Large and Persistent Carbon Sink in the World’s Forests. Science 333, 988-993.

          Yude Pan and colleagues report the estimated amount of carbon stock in the world’s forests at 861 ± 66 Pg C of which 44% resides in soil, 42% in live biomass, 8% in dead wood, and 5% in litter. Breaking down the C sink by types of forests, tropical forests account for 471 ± 93 Pg C, boreal forests 272 ± 23 Pg C, and temperate forests 119 ± 6 Pg C. Tropical and boreal forests store most of the earth’s carbon, however tropical forests have 56% in above ground biomass and boreal forests only have 20% in above ground biomass. This difference is crucial in determining what precautions should be taken to preserve certain parts of forests in different regions. The annual change in C stock shows an uptake of 2.5 ± 0.4 Pg C per year for 1990 to 1999 and 2.3 ± 0.5 Pg C per year from 2000 to 2007. Despite the overall C uptake in these two time periods, regional differences are apparent. For example, temperate forests increased C sink by 17% more from 2000 to 2007 compared to 1990 to 1999, while tropical forests decreased C sink by 23% during the same time period. By subtracting the C sink losses from forest degradation in tropical areas, the net forest C sink is estimated at 1.0 ± 0.8 and 1.2 Pg C per year from 1990 to 1999 and 2000 to 2007, respectively.
          Examining C sink by region and biome, boreal forests had an estimated C sink of 0.5 ± 0.1 Pg C per year for the past two decades. Some regions, such as Asian Russia, account for a significant portion of the total sink, but experienced no overall change. Other areas, like European Russia, experienced a 35% increase in C sink. The authors suggest this increase could be due to increased forest area after agricultural abandonment, reduced harvesting or several areas of forest progressing to later stages in the plant life cycle. The C sink in Canadian forests reduced by half during the same time period, largely due to wildfires and insect outbreaks. As a result of the increases and decreases mentioned above, the overall C sink did not experience a net change.
          Temperate forests contributed 0.7 ± 0.1 and 0.8 ± 0.1 Pg C per year for the past two decades. This increase in C sink is likely due to increases in density of forest biomass and an increase in forest area. The C sink in the U.S. on average increased by 33% during this time period due to the growth of forest area resulting from previous agriculture and harvesting. However, the western U.S. has experienced forest mortality due to drought stress, insects, and fires. The C sink in Europe remained constant, but the C sink in China increased by 34%, likely due to newly planted forest area and reforestation programs.
          Tropical forests account for about 70% of the world’s forests and in this study, the authors collected data from intensive monitoring of Africa and South America, and used these trends to estimate the data for Southeast Asia. The total C sink in tropical forests is estimated at 1.3 ± 0.3 and 1.0 ± 0.5 Pg C per year for the past two decades. The total C sink during this time period accounts for about half of the total C sink. Tropical land use, including clearing forests for agriculture, timber and pasture areas, accounts for a carbon release second to the amount produced by fossil fuels. Deforestation accounted for about 40% of global fossil fuel emissions in the past two decades, but this is often overlooked because it was offset by a large uptake in C due to forest regrowth. Pan and colleagues estimate that C uptake was stronger in regrowth forests compared to previously intact forests due to simultaneous rapid increases in biomass. The authors also suggest that the state tropical forests has a significant impact on total C sink and better monitoring techniques and increased understanding of C cycling in these areas should be a priority in the future.
          Dead wood, litter, soil, and harvested wood account for about 35% of the world’s forest C sink and are important factors that should not be overlooked, however they remain the most difficult to measure. This measurement could also be too low as it does not include deep soil beyond 1 meter and improved measuring techniques would be necessary to account for this. Dead wood is more vulnerable to fires than other sources of C and harvested wood in boreal areas experienced a decrease over the past two decades, mainly due to decreased Russian harvesting.
          Pan and colleagues recognize critical data gaps in their study including a substantial lack of data for North America (mainly Canadian unmanaged forests and Alaska), and for the C flux in tropical forests, which may account for a 10–20% error in estimates. The authors suggest that in order to attempt to combat these uncertainties, land monitoring should be increased, globally consistent land-sensing is necessary, and scientists need better tools to measure below ground, dead wood and litter sources of C.
          Forests have a crucial role in absorbing atmospheric C and will continue to maintain strong control over atmospheric CO2 levels. The factors that affect C levels in the atmosphere are complex and it is necessary to adopt better monitoring systems to separate their impacts and determine the effects of climate change. The authors note that although a large amount of CO2 humans place in the atmosphere is sequestered by forests, deforestation significantly contributes to C losses and relying on forests to absorb C is not without risk.

Negative Effects of Increased Temperature and O3 Offset Positive Effects of CO2 in Oilseed Rape (Brassica napus L.)

CO2 in the atmosphere is steadily increasing and is predicted to be 500–1000 ppm by the end of the century. Emissions of other greenhouse gases are also increasing and are expected to raise the surface temperature 1.8–4.0o C, along with increasing emissions of ozone (O3) from human activity. These forces, and many others, naturally act together and have an important effect on agricultural productivity and climate change. It is more useful and practical to study the effects of multiple, layered factors of climate change than to study one factor in isolation. For example, increased CO2 alone will increase the photosynthetic rate in plants, increasing biomass production, and result in positive growth for plants. However, this increase in biomass does not necessarily lead to an increase in crop yield. It is important to combine and test the effects of various factors of climate change on crops to determine potential crop yield because with a growing human population, maximizing crop yield is highly desirable. Plants do not have many natural adaptations for living in conditions with increased CO2, so it is important to study how they react in order to better breed and genetically prepare plants for climate change.—Taylor Jones
Frenk, G., Van der Linden, L., Mikkelsen, T. N., Brix, H., Jorgensen, R. B., 2011. Increased [CO2] does not compensate for negative effects on yield caused by higher temperature and [O3] in Brassica napus L. European Journal of Agronomy 35, 127–134.

          Frenk and colleagues controlled the ambient conditions of four cultivars of oilseed rape (Brassica napus L.) of different ages and origins and exposed each cultivar to a different combination of increased CO2 (700 ppm), increased temperature (+5oC), and increased O3 (60 ppb). The plants were raised in growth chambers and at the end of maturation, ten plants from each cultivar were selected at random to study. The pod, stem height, and stem width were recorded along with seed yield, stem weight, and biomass. The Thousand Seed Weight (TSW) and Harvest Index (HI) were determined for each sample.
          Increased temperature alone generally reduced the seed yield by 38–58%, the total number of seeds, and the mass of seeds and pods. Despite these general trends, variability among cultivars only produced a significant difference in seed yield for two of them. Stem biomass was not significantly different with increased temperature, and only one cultivar showed a difference in stem weight. The low total seed yield also reduced the HI. The authors predict the decrease in biomass typically associated with increased temperatures is due to reduced rates of photosynthesis, quick development, increased respiration, and decreased organ development. Plant breeding today is often focused on yield, so these new plants will likely be the most susceptible to climate change and the negative effects of increased temperature.
          Increased CO2 alone resulted in a general increase in total seed yield (only significant for one plot) and the total number of seeds. Stem height increased for all cultivars and biomass increased in general, but was only significant for one cultivar. Frenk et al. predict that the effects of increased CO2 can be offset over time because the plant does not have enough storage organs and has reduced carbon sink capacity.
          Increased O3 alone had no effect on plant yield or stem weight, but combined with temperature, O3further reduced the positive effects of increased CO2, and further decreased yield. When CO2 and temperature both increased, they equalized the effects of one another and the sample resembled the control in biomass growth and yield. According to Frenk and colleagues, no study to date has examined the combined effects of the three factors discussed above on agricultural productivity and the results show significant changes in agricultural productivity and should be combined with more abiotic and biotic factors in the future to determine the full effects of increased CO2.

Elevated CO2 Leads to Long-Term Forest Productivity and Increases in Carbon Flux

With rising levels of atmospheric CO2 due to climate change, the earth is becoming more dependent on changes in ambient air composition and its effect on plant growth and productivity. Recent studies have shown significant variety in ecosystem responses to enriched CO2 environments and only some studies demonstrated increased rates of NPP. In the following experiment, Drake et al. (2011) examine the physiological responses of loblolly pine (Pinus tadea) trees to increased CO2 and determine the effects on nutrient availability and uptake. The experiment was performed on the grounds of Duke’s FACE program and the authors collected data on a variety of physiological plant factors in ambient and enriched CO2 to determine if the information from this testing site can be applied to other ecosystems. It was predicted that increases in carbon flux, nitrogen-uptake and overall plant productivity would lead to long-term forest enrichment. —Taylor Jones
Drake, J. E., Gallet-Budynek, A., Hofmockel, K.S., Bernhardt, E. S., Billings, S. A., Jackson, R. B., Johnsen., K. S., Lichter, J., McCarthy, H. R., McCormack, M. L., Moore, D. J. P., Oren, R., Palmroth, S., Phillips, R. P., Pippen, J. S., Pritchard, S. G., Treseder, K. K., Schlesinger, W. H., DeLucia, E. H., Finzi, A. C., 2011. Increases in the flux of carbon belowground stimulate nitrogen uptake and sustain the long-term enhancement of forest productivity under elevated CO2. Ecology Letters 14, 348–357.

          John E. Drake and colleagues started the experiment with 3-year-old loblolly trees planted 2.4 by 2.4 meters apart. In 1994, they began collecting data on the paired reference plots and in 1996, began collecting data in all additional plots. Some data was taken from previous research at the FACE testing site and some data was new for this experiment. The standing pool of fine root biomass was measured every three months by collecting a 4.65 cm block of soil 15 cm deep and analyzing it for C content. The amount of C stored as CO2 in the soil air space was calculated and the microbial biomass of N was measured.
          The rate of CO2 diffusion out of the soil (soil CO2 efflux) was measured with the closed IKGA system and the data were plotted as a temperature response curve. The fine root production was measured monthly and the production of various fungi was measured using microscopic methods. The on-site litterfall was collected monthly January–September and biweekly October–December in 12 baskets per site, measuring 0.218m2 each. The authors also collected data on C-cycling, NPP and total belowground carbon flux (TBCF).
          The results showed that as CO2increased, the rate of C-cycling through the soil increased by 17%. Also, the TBCF increased 16% and the increased C entering the soil in an enriched CO2  environment led to increases in the net biomass. N also increased, supporting an increase in NPP, supplied by a 25% increase in soil uptake. TBCF and N-uptake demonstrated an inverse relationship. NPP positively correlated with canopy N content and supported an increase in photosynthetic N-use efficiency.
          Drake et al. suggest that the increase in productivity is due to an exchange of tree C with soil N belowground, allowing the N levels to meet the growth requirements of the plant. Also, the long-term NPP increases are likely enabled by increases in TBCF that stimulate N-uptake and  canopy leaf area. Despite increased productivity, the experiment did not result in a net accumulation of  C in the mineral soil pool. The authors suggest this could be a result of the fixed C being added to the experiment replacing some of the C initially present in the soil and increases in microbial activity could account for changes in the soil composition. This effect on C pools is likely to model the response of soil to a long-term rise in CO2. The authors recognize that this study provides an initial attempt to examine the physiological effects of increases CO2, but is by no means comprehensive and further experiments representing a diversity of effects are necessary to better understand the long-term effects of increased CO2. A simple experimental framework describing the most important processes that effect N availability and C uptake is necessary to understand the effects of CO2 enrichment in the future.