The 100th meridian bisects the Great Plains of the United States and effectively divides the continent into more arid western and less arid eastern halves and is well expressed in terms of vegetation, land hydrology, crops, and the farm economy. Here, it is considered how this arid–humid divide will change in intensity and location during the current century under rising greenhouse gases. It is first shown that state-of-the-art climate models from phase 5 of the Coupled Model Intercomparison Project generally underestimate the degree of aridity of the United States and simulate an arid–humid divide that is too diffuse. These biases are traced to excessive precipitation and evapotranspiration and inadequate blocking of eastward moisture flux by the Pacific coastal ranges and Rockies. Bias-corrected future projections are developed that modify observationally based measures of aridity by the model-projected fractional changes in aridity. Aridity increases across the United States, and the aridity gradient weakens. The main contributor to the changes is rising potential evapotranspiration, while changes in precipitation working alone increase aridity across the southern and decrease across the northern United States. The “effective 100th meridian” moves to the east as the century progresses. In the current farm economy, farm size and percent of county under rangelands increase and percent of cropland under corn decreases as aridity increases. Statistical relations between these quantities and the bias-corrected aridity projections suggest that, all else being equal (which it will not be), adjustment to changing environmental conditions would cause farm size and rangeland area to increase across the plains and percent of cropland under corn to decrease in the northern plains as the century advances.

To project the future we need models. These can range greatly in complexity, but for future climate change the best guidance comes from the coupled atmosphere–ocean–land–sea ice models of the CMIP5. Here in Part II, we will use the CMIP5 models to compute projections of the change in aridity and aridity gradient for the next century. However, we should never use these models blindly, and instead we should be fully aware of model biases and limitations. Often a “bias correction” is needed and one will be applied here to estimate the future aridity index. We will then use simple relations between aspects of the agricultural economy and the aridity index to suggest the implications of the changes in climate. The work suggests that the 100th meridian in effect moves steadily east. The physical reasons for why this is so will be determined. The implications are that, all else being equal (which it will not be), cultivation of wheat and rangelands will expand east at the expense of corn and that farm size will need to increase to reflect the new climate and land productivity.

The 100th meridian as the arid–humid divide was a description of the late-nineteenth-century climate and landscape that has remained valid at least into the beginning of this century. But now climate change caused by rising greenhouse gases from fossil fuel burning is advancing. Based on the most recent climate model projections from phase 5 of the Coupled Model Intercomparison Project (CMIP5) and analyzed by the Intergovernmental Panel on Climate Change (IPCC) Fifth Assessment Report (AR5), many workers have reported that North America will see, over the coming decades, a marked transition in hydroclimate. Precipitation is expected to decline in southwestern North America but increase in the northeast, and temperature will rise everywhere ( Seager et al. 2013 ; Maloney et al. 2014 ; Seager et al. 2014 ). Cook et al. (2015) used the CMIP5 model ensemble to show that these changes combine to cause a quite alarming increase in aridity in the plains as measured either by the Palmer drought severity index (utilizing the Penman–Monteith formulation for potential evapotranspiration) or in the actual modeled soil moisture. Under such climate change we would expect the modeled arid–humid divide to move or the “effective 100th meridian” to advance eastward. Given that the aridity gradient is expressed in the agricultural economy, this could necessitate farms to adapt to new environmental conditions, by consolidation and changes in crops grown, for example, or risk becoming unprofitable. Disruption could be minimized if the climate changes and agricultural economic implications were anticipated in advance.

The 100th meridian was conceptualized by the nineteenth-century explorer, scientist, and director of the U.S. Geological Survey and Bureau of Ethnology John Wesley Powell as the clearly demarcated divide between America’s arid west and humid east ( Powell 1879 , 1890 ). In Part I of this two-part paper, we showed the validity of this conceptual divide in terms of a sharp zonal gradient in aridity across the Great Plains, elucidated the physical processes in the atmosphere that establish the aridity gradient, and examined how it is expressed in terms of land surface hydrology and vegetation and, finally, how it is realized in terms of the agricultural economy. It was found that, on all scores, the 100th meridian does indeed represent a divide in the physical character and social and economic structure of the central United States. Powell used the 100th meridian to argue that plans for settlement and development of the arid land west of the meridian should be different to those applied to the East and be very conscious of the constraints imposed by aridity and the need for irrigation in the presence of limited water availability. While his ideas were largely ignored ( Stegner 1954 ), apparently it is nonetheless the case that environmental conditions did influence the land development and use over the period since Powell.

We make use of all the models that participated in CMIP5 that provide all the data needed. The need for 6-hourly data to evaluate moisture transports limits the number of models to 18. We use one run from each of the models. The models and some of their details are given in Table 1 . To compare model simulations to the observed state, we analyze the “historical” coupled simulations forced by known and estimated changes in radiative forcing, land use, etc., for 1979 to 2005 and the RCP8.5 business-as-usual projections of the 2006 to 2100 period forced by estimates of changes in climate forcing, assuming no effort is made to reduce greenhouse gas emissions. This scenario is chosen because of the current lack of any enforceable and strong international agreement to combat climate change. All model data were regridded to a common grid. The numerical methods for evaluating moisture transport in the models and ERA-Interim are as in Seager and Henderson (2013) , and computations were done on 6-hourly data. Computations are first done for each model run before averaging in time for each model, as needed, and then across the models to create the multimodel means shown here.

To analyze precipitation, evapotranspiration, and atmospheric moisture transports, we make use of the European Centre for Medium-Range Weather Forecasts (ECMWF) ERA-Interim for the 1979 to 2015 period ( Dee et al. 2011 ). ERA-Interim assimilates multiple sources of atmospheric and surface data into a recent version of ECMWF’s weather forecast model using up-to-date data assimilation methods. Notably, it assimilates satellite-derived, moisture-sensitive irradiances and pays close attention to representing the hydrological cycle. The moisture transports within the ERA-Interim will be compared to those from the climate models.

To compare the models against observations, we use data from the National Land Data Assimilation System 2 (NLDAS-2). The following text follows that in Part I. NLDAS-2 is a land surface model based on land surface hydrology models driven by atmospheric data ( Xia et al. 2012a , b ) available online (at http://ldas.gsfc.nasa.gov/index.php ; last accessed September 2017). Land surface models are physical models of the upper part of the land surface that solve equations for transfer of heat and moisture between the surface and the deeper layers and that also contain a representation of vegetation and interactions between it, the atmosphere, and the soil below. The land surface models are forced by imposed air temperature, humidity, winds, surface radiation, and other quantities. In this case atmospheric data from the National Centers for Environmental Prediction (NCEP) North American Regional Reanalysis (NARR) reanalysis ( Mesinger et al. 2006 ) are used in combination with precipitation data developed by the PRISM Climate Group at Oregon State University [details of which can be found at http://www.prism.oregonstate.edu and in Daly et al. (2000) ]. The data period covers 1979 to 2015, and the spatial resolution is ⅛° in latitude and longitude. The atmospheric data were used by NLDAS-2 to force three different land surface models, Mosaic, VIC, and Noah, but, for brevity, as in Part I, we only present results using the Noah model. For farm economy we examined type of agricultural use, crops grown, and farm numbers and size using the USDA/National Agriculture Statistics Service 2012 Census of Agriculture data at the county level ( www.agcensus.usda.gov/Publications/2012/Online_Resources/Ag_Census_Web_Maps/Overview ; last accessed 30 September 2017). For nonfederal rangelands, defined as grasslands that provide forage for grazing animals, we used data from the USDA Natural Resources Conservation Service (available at https://www.nrcs.usda.gov/wps/portal/nrcs/detail/national/technical/nra/nri/?cid=stelprdb1253602 ; last accessed 30 September 2017). This provides rangeland area in hectares, which we convert to the percent of rangeland for each U.S. county.

It is of interest to determine the physical causes of the change in AI. To do this we compute projections of AI, allowing P and PET to change one at a time. For this, we define as the model AI for the future, allowing only P to change and keeping PET at historical values, and as the model AI for the future, allowing only PET to change and keeping P at historical values. These are

As we shall see, ⁠, the CMIP5 model AI for the historical period, has significant biases compared to that from NLDAS-2 ⁠, including a much weaker zonal gradient. To examine future changes in the AI, we wish to preserve the spatial features of the observed historical period and hence adopt a bias correction methodology. We will use the CMIP5 models to evaluate the fractional change in AI at each latitude and longitude and then adjust the long-term 1979–2015 climatological NLDAS-2 AI, denoted by ⁠, by the CMIP5 modeled fraction. Hence, for each season, year, and model, we compute

where the variables for are taken from NLDAS-2 or CMIP5. The term is net surface radiation, G is ground heat flux (unavailable for the models and set to zero), is air temperature, is wind speed above the surface, is the saturation vapor pressure at and is the actual vapor pressure (both in mb), is the slope of the saturation vapor pressure curve with temperature, and γ is the psychrometric constant. Unlike for NLDAS-2, we found that for some models it was necessary to set a minimum vapor pressure deficit in order to prevent very small or negative PET and extreme large and/or negative values of AI. A minimum value of 0.1 mb (considerably less than typical minimum winter values of 1 mb or more) was imposed.

The aridity index (AI), which equals precipitation P as a fraction of potential evapotranspiration ⁠, ⁠, was defined in Part I, where we evaluated it using monthly data from the observationally based NLDAS-2. Here, we will use data from both NLDAS-2 and from the CMIP5 models and compute AI for both based on monthly data. AI is evaluated using seasonal means of P and PET. For the models we have the simulations of the historical period and the projections of the future. Hence, using subscripts h and f to refer to historical and future and N to refer to NLDAS-2, we have ⁠. Similarly for the CMIP5 models, denoted by subscript C, we have and ⁠. PET for both NLDAS and CMIP5 is computed using the Food and Agriculture Organization version of the Penman–Monteith equation (see Allen et al. 1998 ). This is given by briefly dropping the N and C subscripts:

In Part I, we showed using maps that there was a notable west–east gradient in farm size and rangeland coverage, at all latitudes, and percent of cropland under wheat or corn, in the northern plains, that was associated with the aridity gradient. To examine how changes in AI will impact the agricultural economy we will first use the historical data to examine farm size, rangeland coverage, and percent of crops under corn as a function of the AI. This will be done separately for the southern, central, and northern plains, with the expectation that we will see different relationships. We will then fit polynomials to the data distributions. We will then use the future bias-corrected AI projections and the polynomial relations developed on observed historical data to project future farm size, rangeland coverage, and percent of crops under corn. For the historical relations it is reasonable to suppose that they reflect an adjustment of the farm economy to prevailing environmental conditions. The projections therefore simply assume that the future farm economy will undergo a similar adjustment to changing environmental conditions and ignore other changes (technological change, economic adjustment, subsidies, etc.) that could also be influential. Our goal here is to provide a simple illustration of plausible change and not a prediction of actual expected change, which will additionally be affected by other factors such as changes in technology and plant water-use efficiency caused by fertilization.

To examine the relations between model ⁠, and moisture transports, in Figure 3 we plot annual-mean P, actual evapotranspiration E, and for NLDAS-2, ERA-Interim, and the CMIP5 multimodel mean and the vertically integrated moisture transport for ERA-Interim and the multimodel mean. In a steady state, the convergence of the vertically integrated moisture transport balances ⁠. At the surface, in steady state and the absence of a moisture source for the atmosphere (e.g., oceans and lakes), must be positive and balanced by runoff. Relative to NLDAS-2, the models are too wet across the west and too dry in the Midwest, decreasing the zonal gradient of P. Comparing the ERA-Interim and model moisture transports it is seen that, in the northwest, the models do not simulate the coastal trapping of moisture incoming from the Pacific Ocean by the coastal ranges and instead allow too high precipitation to extend too far inland to the east. Too much moisture also leaks into the interior west from the Pacific Ocean across California and Mexico (see also Sheffield et al. 2013 ). More generally, the models have excessive P across much of the continent with the exception of the Gulf Coast. This is not attributable, in general and clearly, to erroneous moisture transport from the oceans to the continent, except across western mountains. Instead, the excess P goes along with excess E. Sustaining excess P with excess E allows for less of a bias in (and, hence, runoff), and model compares more favorably with NLDAS-2 than does P or E. (The ERA-Interim is unphysically negative in the western plains and the southwest, which emphasizes the difficulty data assimilation schemes have handling the hydrological cycle.) Regardless, the conclusion is that the models recycle too much moisture between the land surface and precipitation. Excess recycling increases P. If PET was unchanged, increasing P would increase AI. However, too much recycling also causes excess ET and, hence, surface cooling that could reduce PET and further increase AI.

Next, as in Part I, we recompute for each model AI while setting all quantities except 1) VPD and 2) P to their zonal-mean values for the season and year and then average across the models. This allows determination of the causes of zonal variations in AI within the model ensemble mean. Figure 2 shows the AI that derives from zonal variations in VPD alone and the AI arising from zonal variations in P alone for both NLDAS-2 and the CMIP5 multimodel mean. Both contribute to the model biases in simulating the AI field. The models underestimate the tendency to aridity introduced by high VPD in southwestern North America and extending into the southern and central plains. Errors in the precipitation simulation make the too high across the interior northwest, the northern plains, and southwest and southern plains. This is no doubt, in part, because of the low model resolution not representing the topography of the coastal ranges and their ability to wring out moisture. In general, the models underestimate how dry the interior west of North America is. The models also overestimate in the southeast and Appalachian region.

Comparing the annual-mean PET, and AI to those derived from NLDAS-2 ( Figure 2 ), it is clear the models fail to simulate the stark west–east AI gradient across the plains. In the central and northern plains there are regions of too high AI to the west and too low AI to the east of the 100th meridian. The bias originates in 1) far too high AI in the interior northwest, 2) AI values that are not low enough in the western plains at all longitudes and in the southwest, and 3) too weak a gradient of increasing AI from the central to eastern plains (even as the models overestimate AI in the Appalachian region).

We begin by examining how well the current generation of climate models (those participating in CMIP5) simulate P, PET, and the AI. Figure 1 shows these by season for the multimodel average across the CMIP5 models, and Figure 2 shows annual-mean values and, for comparison, those from NLDAS-2. The precipitation distribution, with the wettest conditions in the Pacific Northwest and southeast in winter and spring and drier conditions in the southwest and interior west year-round, is qualitatively correct. Also qualitatively correct is the more zonal pattern of PET with declining values from south to north and the development of high PET regions in the southwest and southern plains in summer. The model AI shows vast areas of highly positive values in the northwest and east during fall and winter separated by a central region of lower values that spreads into the southwest and widespread values less than 1 in the spring and summer with minimum values in the southwest.

To look at the temporal evolution of the aridity gradient we average the AI over latitude for the northern (⁠ ⁠), central (⁠ ⁠), and southern (⁠ ⁠) plains. The time span covers 1979 to 2100 and so shows the actual NLDAS-2 AI followed by the bias-corrected AI from 2016 on. A time smoothing has been applied primarily to reduce the year-to-year variability that is strong in NLDAS-2. The model projections are an average across models and, in contrast, are relatively smooth in time because of isolating the forced response. The resulting Hovmöller plots are shown in Figure 7 . The general decrease in AI is clear at all longitudes as well as the muting of the zonal gradient, while the eastward shift of AI values is most evident in the southern and central plains and less so in the north. Nonetheless, in terms of AI value, the effective 100th meridian progressively moves east as the century advances. 1

The changes in P alone tend to reduce AI in the southern part of North America, most strongly in the Gulf states, and increase AI across northern North America, most strongly in the Northeast. There is considerable model agreement on these changes. These patterns are somewhat different to changes in P alone (see Seager et al. 2014 ) because of the seasonal weighting by PET, which provides preferential weighting to the cooler, low PET, seasons. The P-induced changes in AI only modestly weaken the AI gradient across the southern plains. In contrast, the PET-induced changes in AI cause a notable decline everywhere in Mexico and the United States and also a weakening of the west–east gradient as AI declines more east of the 100th meridian than west (again with considerable model agreement). This is because a given change in PET will yield a larger change in AI in the east, where the historical PET is smaller and the historical AI is larger than in the west. The models agree everywhere that climate change will increase PET and tend to reduce AI. This is no doubt because of the dominant influence of rising temperature and vapor pressure deficit on PET ( Cook et al. 2014 ).

What are the main causes of the change in AI? To examine this we recompute the bias-corrected AI holding, for each model, the PET fixed at the climatological 1979–2015 value but allowing P to change to create and then allow PET to vary while holding P at the climatological value to create (see section 3 for the details). Figures 5 and 6 show the maps of and and their change relative to the historical period in the same format as for the total changes in Figure 4 .

In Figure 4 , we show maps of the bias-corrected AI averaged over 2021–40, 2041–60, 2061–80, and 2081–99 as well as the differences between these periods and the 1979–2015 NLDAS-2 ⁠. Notably the essential spatial structure of AI with the marked zonal gradient in the plains remains over the course of the twenty-first century. However, comparing to the 1979–2015 AI map in Figure 3 , there is a noticeable eastward encroachment of low AI into the western plains, while the region of moves east across the borders of South Dakota–Minnesota, Nebraska–Iowa, Kansas–Missouri, Oklahoma–Arkansas, and Texas–Louisiana. There is a striking increase in the relative aridity (lower AI) in the Gulf Coast states and Appalachia and parts of the Midwest. This is easily seen in the maps of change in AI, where it is also noticed that AI declines more in the east than in the west of the United States. As such the aridity gradient not only moves eastward but also becomes more muted. By midcentury there is widespread model agreement on these changes away from the locations where the projected change is small.

As expected for the southern and central plains the changes in AI do not lead to projected changes in the percent of cropped land under corn because of the absence of dependence of the latter on AI or longitude in the historical period. In the northern plains, where the U.S. Corn Belt encroaches in the east and corn can reach over 50% of cropped land, declining AI leads to little change in the percent of corn in the near future but a decline of up to a few percent later in the century. Although not shown, the same methodology projects that wheat cropping would expand in the cropland vacated by corn. In all regions of the plains, and primarily east of the 100th meridian, the naive model suggests an increase in the percent of land under rangeland as aridity increases.

The bias-corrected projections of AI can then be used to infer from the curves in Figure 8 the projected future changes in farm size and percent of cropped land under corn. That is, we first develop the current functional relations: ⁠, where is current farm size, is current percent cropped land under corn, is current percent county under rangeland, and are the polynomial functions in Figure 8 . The projections are then ⁠. Figure 9 then shows the farm size, percent cropped land under corn, and percent county under rangeland as a function of longitude for the present and two-decade periods during the current century. The varying strength of the dependence of farm size on AI introduces interesting latitudinal structure to the projections of increase in farm size. While AI decreases most in the southeastern plains (where farm size is projected to increase), the largest increase in farm size is projected for the southwestern plains because here, while the decrease in AI is smaller, the historical relation between decreasing AI and increasing farm size is very strong ( Figure 8 ). In the southwestern plains, this naive model would suggest farms will need to increase their size by a quarter to a third to restore equilibrium with the increased aridity. In the central and northern plains, the decrease in AI is less, and the sensitivity of farm size to is AI weaker, and these combine to give consistent but modest projections of increases in farm size on the order of 10%.

To assess how the projected changes in AI might impact the farm economy, we will use statistical relations described by the third-order polynomial curves that best fit the observed farm variable–AI relations. These curve fits are also shown in Figure 8 for the three farm quantities and three regions of the plains. Consistent with the maps shown in Part I, at all latitudes there is a decrease in farm size as AI increases. This is the reflection in farm–AI space of the decrease in farm size from west to east across the plains, as expected in terms of the area of operation required to achieve profitability in the face of lower aridity and increased land productivity. In the southern and central plains, there is little relation between the percent of cropped land under corn and AI. This reflects the small area under corn in the south and the “Nebraska exception”—high percentage of corn cropping in an arid area caused by accessible groundwater and irrigation—in the central plains. However, in the northern plains there is a clear increase of the percent of cropped land under corn as AI increases, reflecting the transition from wheat cultivation in the northwest plains to corn cultivation in the northeast plains (see Part I).

In Part I, we showed maps that demonstrated how farm size, number of farms, rangeland coverage, and percent of cropland used to grow wheat or corn have evolved to reflect the sharp west–east aridity gradient across the plains, albeit with notable exceptions (e.g., Nebraska where irrigation from the Ogallala Aquifer allows cultivation of corn in a dry state). Here, we present the same data in a different way by plotting in Figure 8 , for the northern, central, and southern plains, the farm size, percent of the county under rangeland, and percent of cropland under corn as a function of the NLDAS-2 AI. Each data point is the average across latitude and longitude for a 1° longitudinal bin.

The 100th meridian was shown in Part I to be a stark divider between a more arid west and more humid east that is expressed well in the natural landscape and also in the farm economy. While the plains have experienced a never-ending variation between times of drought and times of pluvial (Cook et al. 2007; Stahle et al. 2007; Seager et al. 2005; Herweijer et al. 2006; Schubert et al. 2004; Forman et al. 2001) in which the aridity gradient would have changed in intensity and location, it appears that agriculture has evolved in a way that the size of farms, and how the farm land is used, responds to the mean aridity gradient. However, in recent decades, human-induced climate change has been added onto this natural variability. The United States has broadly warmed (apart from the southeast; Capparelli et al. 2013), while radiatively forced precipitation changes have been modest to date (with a slight reduction in the southwest; Seager and Hoerling 2014). Consequently, we argue that the farm economy has come into rough statistical equilibrium with the spatially varying aridity intensity of the plains and the oscillations between drier and wetter years. This reasoning also implies that the farm economy will evolve as the climate conditions of the plains respond to rising greenhouse gases. To determine what might happen requires projections by models of future conditions. This in turn requires an assessment of how well models can simulate the aridity intensities of the plains. In this paper we assess the ability of the current generation of state-of-the-art climate models that participated in CMIP5 to simulate North American climate, focusing on the plains, and also develop statistical relations between aspects of the farm economy and aridity. Finally, we develop bias-corrected projections of aridity and use these to develop simple projections of the farm economy variables over the current century. The conclusions are as follows:

Climate models generally fail to correctly simulate the amplitude and spatial variation of aridity, measured by ⁠, across North America. While they tend to have reasonably realistic PET, which is primarily influenced by temperature, they tend to overestimate P because of excessive continental E and are unable to simulate the trapping of wintertime eastward moisture advection from the Pacific by the coastal ranges. As such, the models overestimate AI, underestimate its gradient across the plains, and fail to demarcate the stark contrast across the continent between an arid west and a humid east with the 100th meridian as the well-defined, semiarid, subhumid border.

To preserve the gradient in the projections of AI we developed a bias-corrected method that altered the observations-based AI from NLDAS-2 by the fractional difference between the CMIP5 multimodel means for the future and the 1979–2015 historical period. The bias-corrected projections show an overall decrease in AI (increase in aridity) across Mexico and the United States.

When the model projections of future AI are decomposed into contributions from changes in P and PET it is shown that the change in P causes increased aridity across southern North America and decreased aridity to the north but that rising PET (caused by atmospheric warming) causes increasing aridity everywhere.

Because of the greater AI and smaller PET in the east than the west, the projected cross-continent increases in PET cause aridity to increase by more in the east than the west. This reduces the strength of the west–east aridity gradient across the central part of the continent. It also means that the effective 100th meridian—that defined by an aridity level as opposed to a specific longitude—moves progressively east as the century progresses.

Aspects of the farm economy well reflect the west–east aridity gradient. Across the plains, farm size increases as aridity intensifies (to the west). In the northern plains, as aridity declines from west to east, cropped land is increasingly used to grow corn instead of wheat. Given the reasonable assumption that the farm economy evolved over the past century and more to adjust to the environmental conditions, it is expected that it will evolve further in coming decades as those environmental conditions progressively change toward heightened aridity. A simple projection of the current farm economy–AI relations into the future predicts that farm size will need to increase across the plains, but especially in the south, and that in the northern plains there will be a shift toward wheat cultivation and away from corn. Rangeland would expand to the east. The changes in farm size and percent of cropland under wheat or corn are coupled. The value of production and profit per acre are higher for corn than for wheat (see USDA data at https://www.ers.usda.gov/data-products/commodity-costs-and-returns/), and hence a shift from corn to wheat will require an increase in farm size to maintain farm profitability. Across the plains but primarily east of the 100th meridian the projections suggest increased percent of land under rangeland. The current west–east gradients in farm size, choice of crop, and rangeland already reflect environmental reality, and so the projected environmental-driven changes make sense, all else being equal.

There are many caveats that should be attached to this work and its conclusions. First, we have shown that state-of-the-art models simulate the aridity gradient across North America poorly. Hence, even though we have applied a bias correction to the projections to remove the mean state bias, it can be questioned whether these models should be trusted to properly simulate the changes. In response we would say that the model error that leads to an incorrect mean state aridity arises from the precipitation simulation, while the projected aridity change arises most strongly from the temperature and vapor pressure deficit change, which we suspect is more faithfully simulated. Second, while current Earth system models (the subset of all climate models that simulate, in varying degrees of complexity, vegetation and carbon dynamics) predict widespread declines in soil moisture and increases in continental aridity, they also simulate increases in net primary productivity (Scheff et al. 2017; Mankin et al. 2017). This is because, within the models, the beneficial effects on photosynthesis and water-use efficiency of increased overwhelm the effects of increased temperature and vapor pressure deficit. Hence, perhaps, the aridity gradient as expressed in vegetation and crops will not move east as suggested here on the basis of a simple metric like AI in which the computation of PET does not account for biophysical changes. In response, we would say that effects thus far appear to be highly geographically variable (Zhu et al. 2016) and that models quite conceivably overestimate the biophysical response to [see review by Cook et al. (2016) and discussions in Scheff et al. (2017), Mankin et al. (2017), and Allen et al. (2015)]. However, it is also likely that enhanced is increasing crop water-use efficiency to some degree and may alter the relationship between the farm economy and AI. Third, the farm economy projections do not account for changes in crop technology, farming practice, farm policy, and the wider economy. In response we would say that this is an entirely valid criticism, and we emphasize that the farm projections are “naive” and merely attempt to illustrate how, all else being equal, the farm economy would adjust to future changes in AI, given how it has adjusted to prevailing AI over past decades. That said, complex calculations that use a computable general equilibrium model of the U.S. farm economy driven by climate model projections (Malcolm et al. 2012) also conclude that there will be a shift from corn to wheat in the area that our naive methods project the same transition. However, the projected expansion of rangelands eastward may be restricted because this is into lower regions with higher daytime maximum and nighttime minimum temperatures that could stress cattle (e.g., Gaughan et al. 2010).