Climate change in MATOPIBA region of Brazil using Thornthwaite (1948) classification | Research Square window.SnipcartSettings = { analytics: { enabled: false } }; (function() { var accessVector = localStorage.getItem('access_vector') || ''; window.dataLayer = window.dataLayer || []; if (accessVector) { window.dataLayer.push({ user: { profile: { profileInfo: { snid: accessVector } } } }); } })(); (function(w,d,s,l,i){w[l]=w[l]||[];w[l].push({'gtm.start':new Date().getTime(),event:'gtm.js'});var f=d.getElementsByTagName(s)[0],j=d.createElement(s),dl=l!='dataLayer'?'&l='+l:'';j.async=true;j.src='https://www.googletagmanager.com/gtm.js?id='+i+dl;f.parentNode.insertBefore(j,f);})(window,document,'script','dataLayer','GTM-K279D39R'); Browse Preprints In Review Journals COVID-19 Preprints AJE Video Bytes Research Tools Research Promotion AJE Professional Editing AJE Rubriq About Preprint Platform In Review Editorial Policies Our Team Advisory Board Help Center Sign In Submit a Preprint Cite Share Download PDF Research Article Climate change in MATOPIBA region of Brazil using Thornthwaite (1948) classification LUCAS Eduardo OLIVEIRA-APARECIDO, Alexson Filgueiras Dutra, Pedro Antonio Lorençone, and 3 more This is a preprint; it has not been peer reviewed by a journal. https://doi.org/ 10.21203/rs.3.rs-428799/v1 This work is licensed under a CC BY 4.0 License Status: Posted Version 1 posted You are reading this latest preprint version Abstract Identify the climatic characterization of a region and its spatial and temporal variation, as well as its changes in the face of climate change events, is essential for agrometeorological studies because they can assist in the planning of strategies that reduce the negative impacts generated in the cultures exposed to critical climatic conditions. Thus, this study aimed to characterize the climatic conditions of the MATOPIBA region and its changes in scenarios of climate change using the classification index of Thornthwaite ( 1948 ). Daily time series of rainfall and temperature data in the 1950–1990 period were used, arranged in a 0.25º × 0.25º grid, covering 467 points over the studied region. The data set was used to estimate climatological water balance and climate index Thornthwaite ( 1948 ), and obtain the trends climatological according to IPCC (2014) climate change projections, with changes in the average air temperature (+ 1.5°C and − 1.5°C) and precipitation (+ 30% and − 30%). The MATOPIBA region is characterized by its humid, dry subhumid, and Moist subhumid climate, with the rainy seasons, between October and April, and drought, from May to September, well defined. In MATOPIBA climate change scenarios, climatic extreme indices tend to alter the pattern, frequency, and distribution of climate class, which can increase climate risk and impact crop production. Therefore, the results obtained can be used to develop strategies to mitigate the vulnerability of crops to climate change conditions. Climatology Climate Analysis and Modeling Temperature rainfall climate variability climate extreme index northeast of Brazil Figures Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 Figure 7 Figure 8 Figure 9 Figure 10 Figure 11 Figure 12 Figure 13 Figure 14 1. Introduction The Brazilian Cerrado, edaphically characterized by wide territorial extension, flat topography, deep soils with low fertility and high acidity, had and continues to play a key role in the development and expansion of Brazilian agriculture in the national and international agricultural scenario (Vendrame et al. 2013 ). Epicenter of the rapid agricultural expansion mediated by soybean culture, the MATOPIBA region is a continuous area, represented by parts of the Cerrado of the states of Maranhão, Tocantins, Piauí, and Bahia, established in 2015 by Federal Decree 8,447 (Araújo et al. 2019 ; Rauch et al. 2019). This Cerrado region is responsible for an important portion of the Brazilian grain production, where the main agricultural commodities (soybean and corn) stand out in the cultivation areas. Also producing cotton, rice and beans, the MATOPIBA region produced 10.22% of the country's total grains in the 2019/2020 harvest, corresponding to 23.00 million tons, which are mostly destined for the international market (Conab 2020; Silva et al. 2020 ). However, in recent years, these cultivation areas have been impacted by climatic oscillations intensified by rising temperatures and changes in the frequency and intensity of rainfall. The water deficit is common in this region during the summer that negatively affects the growth and development of plants. In this condition, impacts can affect the establishment of the crop after planting and when it reaches the flowering or grain filling stage, it significantly compromises agricultural production (Reis et al. 2020 ; Zilli et al. 2020 ; Wang et al. 2020 ). Climatic condition is one of the factors that most influence agricultural activity in a region (Halder et al. 2020 ). For its identification is necessary to analyze the atmospheric elements that condition the climate of a given locality, being the elements precipitation and air temperature determine the favorable climatic conditions for agricultural crops. Water and air temperature are fundamental factors for plant growth and production, because they participate in processes that affect the photosynthetic rate (Taiz et al. 2017 ). These elements regulate the opening of plant stomatas, affecting the transpiration and respiration processes, causing, under extreme conditions, a reduction in the rate of CO 2 assimilation and the remobilization of stored carbohydrates to tissues of greater demand, affecting the development and plant production (Silva et al. 2020 ). In this sense, the characterization of climatic conditions and their seasonal occurrence in a given region can be strategies to aid in agricultural planning because it is a tool that allows delimiting regions with favorable climatic conditions for agricultural and non-favorable for the cultivation of plants (Tavares et al. 2018 ; Wang et al. 2019 ). To carry out the climatic classification, the frequently used methods involve the indices of Koppen and Geiger (1928), Thornthwaite ( 1948 ), and Thornthwaite and Mather ( 1955 ). The method by Thornthwaite and Mather ( 1955 ) is considered an efficient system in the characterization of different climatic areas because uses the climatological water balance index (CWB) (Elguindi et al. 2014 ; Rolim and Aparecido 2015 ; Sun et al. 2017 ), which makes the method sensitive in the detection of small spatial variations and allows to obtain in a practical and simplified way the storage of water in the soil (Cetin et al. 2020 ). Therefore, its use in agriculture is considered adequate because it considers the plant as a physical medium, since it conducts water from the soil to the atmosphere through transport mechanisms, relating the water needs of the crop to the climatic conditions of the region (Rolim et al. 2007 ). Studies of climatic characterization that use the method of Thornthwaite and Mather ( 1955 ) are fundamental for the understanding of the regions climate, which allows the expansion of new areas of cultivation and the optimization of the productivity of the cultures. However, these studies for the MATOPIBA region are scarce. Thus, we aimed to characterize the climatic conditions of the MATOPIBA region and its changes in scenarios of climate change using the classification index of Thornthwaite ( 1948 ). 2. Material And Methods 2.1. Study area and climate dataset The study was performed in the MATOPIBA region (Fig. 1 ), corresponding to part of the Brazilian Cerrado, with approximately 249,665 km², which includes 337 municipalities with approximately 6 million inhabitants, of which 2 million are residents in the rural area (IBGE 2010 ). To cover the entire MATOPIBA region, climatic data were collected from 1950 to 1990 for the 467 municipalities in the states of Maranhão, Tocantins, Piauí, and Bahia, inserted in this region. Air temperature data (T, °C) and rainfall (R, mm) were collected in the Meteorological Database for Teaching and Research (MDTR) of the National Institute of Meteorology of Brazil - INMET (Brazil 1992). 2.2. Reference evapotranspiration and climatological water balance The reference evapotranspiration (ETo) was calculated using the method of Thornthwaite ( 1948 ), following equations 1 – 6 . $${ET}_{p}=-415.85+23.24T-0.43{T}^{2} for T\ge 26.5 \text{℃}$$ 1 $${\text{E}\text{T}}_{\text{p}}=16{\left(\frac{10\text{T}}{\text{I}}\right)}^{\text{a}} \text{f}\text{o}\text{r} 0 \text{℃}\le \text{T}cript>$$ 2 $$I={\left(0.2\times Ta\right)}^{1.514}$$ 3 $$a=0.4924+1.79\times {10}^{-2} I-7.71\times {10}^{-5} {I}^{2}+6.75\times {10}^{-7}{I}^{3}$$ 4 $$Cor=\left(\frac{ND}{30}\right)\times \left(\frac{N}{12}\right)$$ 5 $$ETo={ET}_{p}\times Cor$$ 6 where ET p is the standard 30-day evapotranspiration (mm 30 days -1 ); N is photoperiod in hours; I and a are thermal indices; T is the average temperature for a given day or period (°C); Ta is the climatological normal annual temperature (°C); Cor is the correction factor; ND is the number of days, and ETo is reference evapotranspiration (mm day -1 ). The climatological water balance (CWB) was estimated for all studied locations, according to the methodology established by Thornthwaite and Mather (1955) (Fig. 2). The maximum available water capacity in the soil of 100 mm was used as a parameter, commonly used, for the purposes of regional climatic characterization (Carvalho et al. 2010; Rodrigues et al. 2018). 2.3. Classification of Thornthwaite ( 1948 ) In the climate classification system of Thornthwaite (1948), reference values were used for the CWB extract, using the annual surplus (SUR year), annual water deficiency (DEF annual) and annual evapotranspiration (PET year) in millimeters (mm year -1 ). These combined variables resulted in the four criteria used for classification (Fig. 3). The first criterion corresponds to the adequacy of humidity (first letter of classification) responsible for determining the nine major climatic types, obtained by calculating the water index (Im, %), indicating the relationship between excess water and water need. The second criterion (second letter of classification) represents the seasonal distribution of humidity, determining the climatic subclass of the region, for the water factor, through the aridity index equation (Ia, %) that relates the water deficit and water need and humidity (Ih). Equations 7 at 9 were used to obtain water (Im), aridity (Ia) and humidity (Ih) indices. $$\text{I}\text{m}=\text{I}\text{h}-0.6 \times \text{I}\text{a}$$ 7 $$\text{I}\text{a}=\left(\frac{DEF yeaar}{ETP year}\right)\times 100$$ 8 $$\text{I}\text{h}=\left(\frac{SUT year}{PET year}\right)\times 1$$ 9 The adequacy of the second class was performed according with water deficit (DEFwinter, DEFsummer) and water surplus (SURwinter, SURsummer) for the seasons summer (⅓DEC + JAN + FEB + ⅔MAR) and winter (⅔JUN + JUL + AUG + ⅔SEP). O terceiro e o quarto critério foram responsáveis por adequar os valores de características termais da região. Para isso, utilizou-se do cálculo da eficiência térmica que relaciona a evapotranspiração potencial anual (PETyear) e concentração da eficiência térmica no verão (PETsummer), resultando na evapotranspiração potencial no verão (Equation 10). The third and fourth criteria were responsible for adjusting the values of thermal characteristics of the region. For that, we used the thermal efficiency calculation that relates the potential annual evapotranspiration (PETyear) and concentration of thermal efficiency in summer (PETsummer), resulting in potential evapotranspiration in summer (Equation 10). $$\text{P}\text{E}\text{T}\text{R}=\left(\frac{PETsummer}{PETyear}\right)\times 100$$ 10 2.4. Climatic sensitivity Climatic sensitivity was developed by change the average air temperature (° C), in + 1.5°C and − 1.5°C, and rainfall (mm), in + 30% and − 30% (Fig. 4 ), according to methodology of Pirttioja et al. ( 2015 ). These values of air temperature and rainfall are future projections reported by IPCC (2014), which make it possible to assess possible changes in future climate and possible impacts on climatic parameters, making it possible to analyze how changes in air temperature and rainfall can influence the climatic classification of the MATOPIBA region. 2.5. Results spatialization Through the geographic information system was performed the spatial interpolation of all climatic elements for all locations using Kriging method (Krige 1951), with spherical model, a neighbor and a spatial resolution of 0.25°, and the system of Albers' equivalent conical cartographic projection. With the overlapping of the maps was possible obtain the climatic maps for the classifications of Thornthwaite ( 1948 ). The development of all the analyzes used in the work followed the steps informed in the flowchart in Fig. 5 . 3. Results And Discussion Average annual air temperatures in the MATOPIBA region vary from 19.8 to 29.1 ºC (Fig. 6). June (Jun) and July (Jul) are the months with the lowest air temperature, with values between 20 and 21 ºC in the southern portion of the region, located mainly in the extreme West of the Bahia state, and of 24 at 28 ºC in portion Center-West and Center-North of MATOPIBA (Figs. 6F and 6G). Elevated temperatures, above 30 ºC, are frequent between September (Sep), October (Oct), and November (Nov) in the Center-North and Northwest portion of MATOPIBA, where the states of Maranhão, Tocantins, and Piauí are located (Figs. 6I, 6J, and 6K). During this period, the occurrence of high temperatures coincides with the higher incidence of solar radiation and lower precipitation, which causes heating of the atmosphere through the emission of long-wave radiation on Earth (Reis et al. 2020). On the other hand, the low temperatures recorded in Jun and Jul can are associated with a lack of precipitation and the consequent reduction in air humidity, which causes less absorption of long wave radiation into the atmosphere at night (Reis et al. 2020). The average air temperature is an abiotic factor that influences the agricultural activity of MATOPIBA because the plants are grown between October (Oct) and April (Apr), a period with high temperatures, where the plants can suffer stress that result in damage physiological, and less growth affecting, consequently, production. For soybeans, the main crop in the region, high temperatures during the rainy season (sowing season) shorten the crop cycle because the rate of degree-day accumulation is faster (Reis et al. 2020). In this sense, tolerant cultivars adapted to high-temperature conditions can be a strategy to keep crops productive on the MATOPIBA agricultural frontier. In the MATOPIBA region, the average annual rainfall is 1,502.75 mm distributed mostly (88.75%) between Oct and Apr (Fig. 7). The highest rainfall levels occur in the Southwest, especially in the region predominated by Tocantins state, with high levels of rainfall distributed evenly during the rainy season (Oct-Apr), varying substantially only in Apr. High rainfall levels are also registered in the Southern of Maranhão and extreme West of Bahia. However, spatial reduction of rainfall indices occurs towards the Northeast region of MATOPIBA, especially in Piauí state, which has an average annual rainfall of 1,080.93 mm. Between May and September (Sep), the lowest levels of rain are observed, below 170 mm, a fact that shows the irregularity in the spatial distribution of rainfall. Rainfall scenario in the MATOPIBA region is modulated by atmospheric systems at different scales, which associated with ecosystem and physiographic factors (as a transition between biomes) strongly influence the intra-seasonal variability of precipitation in the region (Valadão et al. 2017; Reis et al. 2020). However, even though the atmospheric systems formed by the equatorial positioning of the Intertropical Convergence Zone (ITCZ) and the South Atlantic Convergence Zone (SACZ) determine the occurrence of rainfall indices (Grimm 2011; Oliveira et al. 2017), the different levels of rainfall between Southwest and Northeast portion of MATOPIBA can be explained by the fact that the Northeast portion is located in transition biome between Cerrado and Caatinga (semiarid), having less influence of atmospheric systems. However, the Southwest portion is located in the transition of Cerrado and Amazon biomes, with about 100% of its surface in an Amazonian environment (Reis et al. 2020), therefore, influenced by atmospheric systems. Thus, the variable accumulation of rainfall in the MATOPIBA sub-regions is influenced by different vegetative configurations (Reis et al. 2020). Real evapotranspiration is related to rainfall regime of the region because its occurrence is associated with the availability of water in the soil-plant system, being the main way to quantify the loss of water present in soil and plant for atmosphere (Milly; Dunne 2016). Thus, evapotranspiration in the MATOPIBA region occurs more intensely only during the rainy season (Oct-May), with average real evapotranspiration of 1,044.49 mm and a greater quantity of evapotranspirated water in the Southwest of MATOPIBA (Fig. 8). On the other hand, evapotranspiration values less than 40 mm were recorded between Jun and Sep, mainly in the Central and Northeast regions of MATOPIBA. Water surplus in the soil commonly occurs between November (Nov) and April (Apr) (Fig. 9), with a total accumulation of 479.57 mm; in this period, rainfall indices above 100 mm are frequent in MATOPIBA (Fig. 7). The largest water surplus (150 at 200 mm) is concentrated in the Northwest of MATOPIBA, specifically in the areas of Tocantins state that concentrate 47.48% of all water surplus. In Jun, July, Aug, Sep, and Oct there is no water surplus in the region due to low rainfall, an event that characterizes this period as dry season in MATOPIBA (Figs. 9F, 9G, 9H, 9I, and 9J). May presents a water surplus only in the extreme North of MATOPIBA, located in Maranhão, with 48.11% of all annual surplus and an average of 561.32 mm (Fig. 9E). The water deficit is variable during all months of the year (Fig. 10). However, its concentration is greater from Jun to Sep and reaches all MATOPIBA territory, with a deficit average of 267.09 mm, corresponding to 74.44% of all annual water deficit (Figs. 10F, 10G, 10H, and 10I). Water deficit below 5 mm was found in Jan, Feb, Mar, Apr, Nov, and Dec (Figs. 10A, 10B, 10C, 10D, 10K, and 10L), the period in which there are marked volumes of rain. In Oct, the water deficit was zero only in the Southwest of MATOPIBA, represented by Tocantins state; however, in other regions of MATOPIBA, the water deficit can reach 150 mm (Fig. 10J). MATOPIBA region presented climatic classification variable with four distinct classes distributed vertically throughout its delimitation (Fig. 11). Humid regions (class B1 and B2) were classified in 35.04% of MATOPIBA, with subclasses B1wA’a’ (20%) and B2wA’a’ (6%) more frequent (Fig. 13A). Class humid B1 predominated in the South, Central, and North of Tocantins, and occurred in small parts of the territories of Bahia and Maranhão; while the class humid B2 classification was represented only in small portions of West of Tocantins. Moist subhumid (C2) was the second class with the greatest extension in MATOPIBA, distributed in 68.71%, 38.34%, 14.21% and 81.65% of th e Maranhão, Bahia, Tocantins, and Piauí area, respectively (Fig. 11). In addition, it comprised the subclasses C2sA’a’, C2w2A’a', and C2wA’a’, with this latter class more frequently in the region (Fig. 13A). It highlights that these subclasses delimit the areas where the largest producer of soybeans, corn, cotton, and beans are found (Fig. 14), indicating that these classifications have more appropriate climatic conditions for the development and production of crops. Class dry subhumid (C1) represented 12.67% of MATOPIBA, and comprised the subclassifications C1dA’a’, C1s2A’a’, C1sA’a’, and C2rA’a’, being located in the Southwest portion of Piauí and part of West of Bahia. Among the subclasses found, C2wA’a’, B1wA’a’, and C1sA’a’ showed the highest cumulative frequency (around 42%) (Fig. 13A), indicating that the classifications are more comprehensive in MATOPIBA. Air temperature and rainfall volume, in climate change scenarios, altered the climatic characterization of the MATOPIBA region with extinction and/or inclusion of climatic classes (Fig. 12). Scenarios with increased air temperature showed a reduction in areas of climate humid (B1), mainly in Tocantins, and expansion of the Moist subhumid (C2) and Dry subhumid (C1) classes from the East for West of MATOPIBA (Figs. 12A and 12B). In addition, environments characterized as Semiarid (D) were observed in areas of Southwest Piauí and West of Bahia, especially when the scenario was + 3.0 ºC (Fig. 12B). With increasing air temperature, the most frequent climatic subclasses in MATOPIBA were Das’a’, DdA’a’, C1sA’a’, B1wA’a’, and C2wA’a’ which presented an accumulative frequency around 76% (Figs. 13B and 13C). Although these subclasses occur in both + 1.5 ºC and + 3.0 ºC scenarios, greater coverage of the classes Moist subhumid (C2wA’a’), Dry subhumid (C1sA’a’), and Semiarid (das’a’) were found in scenarios of greater temperature increase (Figs. 12B and 13C). These results show that the increase in air temperature alters the climatic conditions of MATOPIBA, which would cause changes in the vegetative configurations of the region, resulting in changes in the transition of biomes, such as reduction of areas of the Cerrado biome and increase of environments with characteristics of biome Caatinga. In addition, the agricultural activity in the region would be drastically affected by climate change caused by the increase in temperature, resulting in risk climatic for the cultivation of plants, thus compromising the production of crops and the agroeconomic development of MATOPIBA. In Thornthwaite climatic index, the rainfall regime becomes the most influential parameter to determine the climatic classes. In scenarios with changes of + 30% in the rainfall regime, the humid class (B4, B3, B2, and B1) occupied 58.14% of the MATOPIBA region (Fig. 12C). However, a greater number of climatic subclasses was found in this scenario, with subclasses C1sA’a’ (Dry subhumid), B2wA’a’ (Humid), B3wA’a’ (Humid), B1wA’a’ (Humid), and C2wA’a’ (Moist subhumid) occurring more frequently (Fig. 13D). The greater coverage of humid class in MATOPIBA environments, in addition to characterizing the extent of the Amazon biome, indicates that the climatic conditions presented would allow to expansion of agricultural areas, increase the number of harvests per year and increase crop productivity. Thus, the increase of + 30% in the rainfall regime becomes the most promising scenario for agroeconomic development in this region. When the scenario is of reduction (-30%) in the rainfall regime, the MATOPIBA region presented the climatic classes Moist subhumid (C2), Dry subhumid (C1), and Semiarid (D), with 40.12% of the area occupied by class C1 (Fig. 12D). The number of subclasses determined was lower with an expressive frequency of C1sA’a’, DdA’a’, DsA’a’, and C2wA’a’ (Fig. 13E). In this scenario, Semiarid environments expanded to areas which were previously classified as Dry subhumid (Fig. 11), in the Center-South portion of Maranhão, Southwest Piauí, and part of West of Bahia. The West region of Tocantins was classified as Moist subhumid, while the Dry subhumid class occupied the Central, North, and South portion of MATOPIBA. In the scenario of lower rainfall, both the Cerrado biome environments and the transition areas, between Cerrado and Caatinga biomes, can be reduced in the MATOPIBA region; however, areas of the Caatinga biome may increase as the Semiard class expands. In addition, the scenario of reduction in the rainfall regime negatively impacts agricultural activity because with low water availability in the soil the plants reduce their photosynthetic efficiency and, consequently, do not reach their productive potential (Taiz et al. 2017). Productive areas located in environments of transition between biomes require technological efforts that encourage an increase in crop production (Araújo et al. 2019), because, in a transition environment between different biomes, ecosystems and climatic conditions are highly diversified, making these areas particularly vulnerable to climate change (Silva et al. 2016). In this sense, areas of MATOPIBA with high production of soy, corn, cotton, and beans would have a strong impact of climate change, since they are located largely in environments of transition from the Cerrado and Caatinga biomes (Fig. 14). Regions of the extreme West of Bahia, South of Maranhão, and Southwest of Piauí present the largest productions of soy, corn, cotton, and beans (Fig. 14), being environments classified as Moist subhumid climate. However, in climate change scenarios with increased temperatures and reduced rainfall, these regions suffer changes in climatic conditions, with transition of climate classes between Moist subhumid, Dry subhumid, and Semiarid (Figs. 12B and 12D). In the perspective of climate change, studies by Zilli et al. (2020) suggest a reduction in crop production, such as soybeans and corn, in areas of the Cerrado biome, mainly in the MATOPIBA region, with the displacement of productive areas to subtropical regions of the Atlantic Forest. However, part of the impact of climate change on MATOPIBA could be offset by increased productivity, which would maintain the agricultural scenario of region. Thus, efforts are required to invest in technology and changes in management processes, such as adapting the sowing schedule for crops, using drought-resistant cultivars, using irrigation, efficiency in crop fertilization, improving structural and soil conditions, soil fertility, and precision agriculture (Zilli et al. 2020). Therefore, following these strategies makes it possible to adapt the crops to the climatic conditions of the region and may increase or maintain the productive potential of the crops, alleviating the impacts caused by climate change. 4. Conclusions MATOPIBA region has air temperature, rainfall and real evapotranspiration averages of 26.28°C, 1,502.75 mm, and 1,044.49 mm, respectively, with the rainy seasons, between October and April, and drought, from May to September, well defined. In addition, this region is characterized by a humid climate (B1 and B2), dry subhumid (C1), and Moist subhumid (C2). However, in climate change scenarios, climatic extreme indices tend to change the pattern, frequency, and distribution of climate class, which can result in increased climate risk conditions for agricultural activity in the MATOPIBA region, generating negative socioeconomic impacts. Therefore, the results obtained can be used to develop strategies to mitigate the vulnerability of crops to climate change conditions. Declarations Compliance with ethical standards Conflict of interest The authors declare that they have no conflict of interest. Funding Statement: This study was financed in part by the IFSULDEMINAS Campus Muzambinho. Availability of data and material: The data/ material is opened Code availability: The software used was python and scripts are available Ethics approval: It is not necessary Consent to participate: All authors approved Consent for publication: All authors approved References Acompanhamento de safra brasileira de grãos. 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Vendrame PRS, Brito OR, Martins ES, Quantin C, Guimaraes MF, Becquer T (2013) Acidity control in latosols under long-term pastures in the Cerrado region, Brazil. Soil Research 51: 253–261. https://doi. org/10.1071/sr12214 Wang C, Linderholm HW, Song Y, Wang F, Liu Y, Tian J, Xu J, Song Y, Ren G (2020) Impacts of drought on maize and soybean production in northeast china during the past five decades. International Journal of Environmental Research and Public Health 17: 2459. Cite Share Download PDF Status: Posted Version 1 posted You are reading this latest preprint version Research Square lets you share your work early, gain feedback from the community, and start making changes to your manuscript prior to peer review in a journal. As a division of Research Square Company, we’re committed to making research communication faster, fairer, and more useful. We do this by developing innovative software and high quality services for the global research community. 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Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-428799","acceptedTermsAndConditions":true,"allowDirectSubmit":false,"archivedVersions":[],"articleType":"Research Article","associatedPublications":[],"authors":[{"id":21655753,"identity":"e692f427-5f85-4889-8231-ada3011d98e5","order_by":0,"name":"LUCAS Eduardo OLIVEIRA-APARECIDO","email":"data:image/png;base64,iVBORw0KGgoAAAANSUhEUgAAAZAAAAAyAQMAAABI0h/eAAAABlBMVEX///8AAABVwtN+AAAACXBIWXMAAA7EAAAOxAGVKw4bAAAAvUlEQVRIiWNgGAWjYBACPgYGAyBlA8SMjQeI0sIG0ZIG0tJAkpbDYA6RWtibNz74ueO83dr2w0BbamyiCWvhOVZs2HvmdvK2M4lALcfSchsIapHIMZPgbbudbHYAqIWx4TARWuTfmEn+bTuXbHb+IbFaJHjMpHnbDtiZ3SDaFp60YmPZM8kJZjeAtiQQ4xd+9sMbH77dYWdvdj794YMPNTaEtYABYwNDIlhlAlHKoVrsiVY8CkbBKBgFIw8AAPnLRNaqaDFpAAAAAElFTkSuQmCC","orcid":"https://orcid.org/0000-0002-4561-6760","institution":"Universidade de Sao Paulo","correspondingAuthor":true,"prefix":"","firstName":"LUCAS","middleName":"Eduardo","lastName":"OLIVEIRA-APARECIDO","suffix":""},{"id":21655754,"identity":"23ea3bde-0707-412c-b311-9784e5c1ac7c","order_by":1,"name":"Alexson Filgueiras Dutra","email":"","orcid":"","institution":"Federal University of Piauí","correspondingAuthor":false,"prefix":"","firstName":"Alexson","middleName":"Filgueiras","lastName":"Dutra","suffix":""},{"id":21655755,"identity":"ebf062d3-6b6f-4d09-bda4-b9100e4ae021","order_by":2,"name":"Pedro Antonio Lorençone","email":"","orcid":"","institution":"Graduate Program in Agronomy – IFMS Campus de Naviraí","correspondingAuthor":false,"prefix":"","firstName":"Pedro","middleName":"Antonio","lastName":"Lorençone","suffix":""},{"id":21655756,"identity":"aae0bed2-f154-4854-88c5-19a2f508130d","order_by":3,"name":"Francisco de Alcântara Neto","email":"","orcid":"","institution":"Federal University of Piaui","correspondingAuthor":false,"prefix":"","firstName":"Francisco","middleName":"de Alcântara","lastName":"Neto","suffix":""},{"id":21655757,"identity":"442d3d11-4ae2-4bfe-b9aa-0d131d5bb54d","order_by":4,"name":"João Antonio Lorençon","email":"","orcid":"","institution":"Graduate Program in Agronomy – IFMS Campus de Naviraí","correspondingAuthor":false,"prefix":"","firstName":"João","middleName":"Antonio","lastName":"Lorençon","suffix":""},{"id":21655758,"identity":"97488297-f3a3-43cd-a40b-39854b5c0c14","order_by":5,"name":"Marcos Renan Lima Leite","email":"","orcid":"","institution":"Graduate Program in Agronomy, Federal University of Piauí","correspondingAuthor":false,"prefix":"","firstName":"Marcos","middleName":"Renan Lima","lastName":"Leite","suffix":""}],"badges":[],"createdAt":"2021-04-16 11:47:00","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-428799/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-428799/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":8199218,"identity":"3da1d21c-039e-4bc3-88d3-682a2e1610b5","added_by":"auto","created_at":"2021-04-19 22:25:59","extension":"png","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":133530,"visible":true,"origin":"","legend":"Geographical location of region MATOPIBA in the states of Maranhão, Tocantins, Piauí, and Bahia, Brazil.","description":"","filename":"floatimage1.png","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/4a930447a713ea3b3b36c8ff.png"},{"id":8199121,"identity":"23f3ee1e-a4bb-41a7-8559-6dd18965c515","added_by":"auto","created_at":"2021-04-19 22:22:59","extension":"jpeg","order_by":2,"title":"Figure 2","display":"","copyAsset":false,"role":"figure","size":163362,"visible":true,"origin":"","legend":"Flowchart of the water balance model modified from Thornthwaite and Mather (1955). Legend: CAD is the soil water capacity (mm), NAC is the negative accumulated (mm), meaning the potential drying of the soil, ALT is the alteration of STO, and i a given period, i-1 previous period.","description":"","filename":"floatimage2.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/cdef33b45a39c25884f088e2.jpeg"},{"id":8199123,"identity":"1ad60f60-c1d3-4ada-be44-a145bd26a015","added_by":"auto","created_at":"2021-04-19 22:23:00","extension":"jpeg","order_by":3,"title":"Figure 3","display":"","copyAsset":false,"role":"figure","size":613180,"visible":true,"origin":"","legend":"Criteria used in the classification of Thornthwaite.","description":"","filename":"floatimage3.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/1f12804b8624bdb4e229f4ab.jpeg"},{"id":8199120,"identity":"ed4987d7-0c5e-4fe5-90af-5536bfa1f8fb","added_by":"auto","created_at":"2021-04-19 22:22:59","extension":"jpg","order_by":4,"title":"Figure 4","display":"","copyAsset":false,"role":"figure","size":20815,"visible":true,"origin":"","legend":"Scenarios of changes in air temperature and rainfall used to determine their influence on the climatic classification of MATOPIBA.","description":"","filename":"4.jpg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/10c5f0efc69155c586498f97.jpg"},{"id":8199221,"identity":"152437a9-4657-4e1d-afeb-bead02c39b3c","added_by":"auto","created_at":"2021-04-19 22:26:00","extension":"png","order_by":5,"title":"Figure 5","display":"","copyAsset":false,"role":"figure","size":70538,"visible":true,"origin":"","legend":"Flowchart representing the steps taken to obtain the Thornthwaite climate classification.","description":"","filename":"floatimage5.png","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/230f6ee4863cf61563fbde9b.png"},{"id":8199132,"identity":"0ac36fed-8613-4e05-a629-9cb45a473d21","added_by":"auto","created_at":"2021-04-19 22:23:00","extension":"jpeg","order_by":6,"title":"Figure 6","display":"","copyAsset":false,"role":"figure","size":485587,"visible":true,"origin":"","legend":"Spatial variability of mean monthly air temperature in the MATOPIBA region of Brazil.","description":"","filename":"floatimage6.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/e0f6d604730075d12cad6fda.jpeg"},{"id":8199220,"identity":"d075ef7d-e9cb-443e-8799-cb53dcde45fb","added_by":"auto","created_at":"2021-04-19 22:26:00","extension":"jpeg","order_by":7,"title":"Figure 7","display":"","copyAsset":false,"role":"figure","size":443761,"visible":true,"origin":"","legend":"Spatial variability of mean monthly precipitation in the MATOPIBA region of Brazil.","description":"","filename":"floatimage7.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/b02918ba58e7d786c738ef88.jpeg"},{"id":8199219,"identity":"c4e004ed-81af-41f0-89b1-b1b42649bb49","added_by":"auto","created_at":"2021-04-19 22:26:00","extension":"jpeg","order_by":8,"title":"Figure 8","display":"","copyAsset":false,"role":"figure","size":470641,"visible":true,"origin":"","legend":"Spatial variability of mean monthly real evapotranspiration in the MATOPIBA region of Brazil.","description":"","filename":"floatimage8.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/a155f6466f4c4dc70ee38fc0.jpeg"},{"id":8199130,"identity":"1d4fbab5-35ef-465b-9b0e-5edeb4ea50d5","added_by":"auto","created_at":"2021-04-19 22:23:00","extension":"jpeg","order_by":9,"title":"Figure 9","display":"","copyAsset":false,"role":"figure","size":464244,"visible":true,"origin":"","legend":"Spatial variability of mean monthly water surplus in the MATOPIBA region of Brazil.","description":"","filename":"floatimage9.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/e6df11bc4609ab3c3e400481.jpeg"},{"id":8199125,"identity":"6fc30ac0-bf4b-4b90-85df-c9101f3f48a7","added_by":"auto","created_at":"2021-04-19 22:23:00","extension":"jpeg","order_by":10,"title":"Figure 10","display":"","copyAsset":false,"role":"figure","size":458661,"visible":true,"origin":"","legend":"Spatial variability of mean monthly water deficit in the MATOPIBA region of Brazil.","description":"","filename":"floatimage10.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/4a0e6a3f8a96aa0eaaff461a.jpeg"},{"id":8199318,"identity":"fcbcedee-679f-4a29-a24c-0fe8e730e973","added_by":"auto","created_at":"2021-04-19 22:29:00","extension":"jpeg","order_by":11,"title":"Figure 11","display":"","copyAsset":false,"role":"figure","size":400596,"visible":true,"origin":"","legend":"Spatial variability of the Thornthwaite (1948) climate index for MATOPIBA region of Brazil.","description":"","filename":"floatimage11.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/1be88829d712f268fdc5c5eb.jpeg"},{"id":8199127,"identity":"30ab64f1-3949-4940-9b4a-2834ad9855c7","added_by":"auto","created_at":"2021-04-19 22:23:00","extension":"jpeg","order_by":12,"title":"Figure 12","display":"","copyAsset":false,"role":"figure","size":424667,"visible":true,"origin":"","legend":"Spatial variability of the Thornthwaite (1948) climate index in scenarios of changes in air temperature and rainfall for MATOPIBA region of Brazil.","description":"","filename":"floatimage12.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/d8b8336074175e24ae382a80.jpeg"},{"id":8199224,"identity":"3173f9a8-857e-4f81-8cb8-61da36904672","added_by":"auto","created_at":"2021-04-19 22:26:00","extension":"jpeg","order_by":13,"title":"Figure 13","display":"","copyAsset":false,"role":"figure","size":379557,"visible":true,"origin":"","legend":"Frequency of the Thornthwaite (1948) climate index in scenarios of changes in air temperature and rainfall for MATOPIBA region of Brazil.","description":"","filename":"floatimage13.jpeg","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/383ca5bcb4754622d76353b1.jpeg"},{"id":8199319,"identity":"62c733fa-e262-47fe-a046-ddd3f2e73ba9","added_by":"auto","created_at":"2021-04-19 22:29:00","extension":"png","order_by":14,"title":"Figure 14","display":"","copyAsset":false,"role":"figure","size":224381,"visible":true,"origin":"","legend":"Spatial variability in the production of the main crops in the MATOPIBA region of Brazil. Source: CONAB (2020).","description":"","filename":"floatimage14.png","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/84656fb5f08543eaf8da0419.png"},{"id":13687449,"identity":"b5852019-1ec8-4347-ab07-9c7d3b82122c","added_by":"auto","created_at":"2021-09-17 12:20:00","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":2219721,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-428799/v1/60d673fa-37df-4e2e-bc76-2f846a9f0b91.pdf"}],"financialInterests":"","formattedTitle":"Climate change in MATOPIBA region of Brazil using Thornthwaite (1948) classification","fulltext":[{"header":"1. Introduction","content":" \u003cp\u003eThe Brazilian Cerrado, edaphically characterized by wide territorial extension, flat topography, deep soils with low fertility and high acidity, had and continues to play a key role in the development and expansion of Brazilian agriculture in the national and international agricultural scenario (Vendrame et al. \u003cspan citationid=\"CR24\" class=\"CitationRef\"\u003e2013\u003c/span\u003e). Epicenter of the rapid agricultural expansion mediated by soybean culture, the MATOPIBA region is a continuous area, represented by parts of the Cerrado of the states of Maranh\u0026atilde;o, Tocantins, Piau\u0026iacute;, and Bahia, established in 2015 by Federal Decree 8,447 (Ara\u0026uacute;jo et al. \u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2019\u003c/span\u003e; Rauch et al. 2019).\u003c/p\u003e \u003cp\u003eThis Cerrado region is responsible for an important portion of the Brazilian grain production, where the main agricultural commodities (soybean and corn) stand out in the cultivation areas. Also producing cotton, rice and beans, the MATOPIBA region produced 10.22% of the country's total grains in the 2019/2020 harvest, corresponding to 23.00\u0026nbsp;million tons, which are mostly destined for the international market (Conab 2020; Silva et al. \u003cspan citationid=\"CR17\" class=\"CitationRef\"\u003e2020\u003c/span\u003e). However, in recent years, these cultivation areas have been impacted by climatic oscillations intensified by rising temperatures and changes in the frequency and intensity of rainfall. The water deficit is common in this region during the summer that negatively affects the growth and development of plants. In this condition, impacts can affect the establishment of the crop after planting and when it reaches the flowering or grain filling stage, it significantly compromises agricultural production (Reis et al. \u003cspan citationid=\"CR12\" class=\"CitationRef\"\u003e2020\u003c/span\u003e; Zilli et al. \u003cspan citationid=\"CR27\" class=\"CitationRef\"\u003e2020\u003c/span\u003e; Wang et al. \u003cspan citationid=\"CR26\" class=\"CitationRef\"\u003e2020\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eClimatic condition is one of the factors that most influence agricultural activity in a region (Halder et al. \u003cspan citationid=\"CR6\" class=\"CitationRef\"\u003e2020\u003c/span\u003e). For its identification is necessary to analyze the atmospheric elements that condition the climate of a given locality, being the elements precipitation and air temperature determine the favorable climatic conditions for agricultural crops. Water and air temperature are fundamental factors for plant growth and production, because they participate in processes that affect the photosynthetic rate (Taiz et al. \u003cspan citationid=\"CR19\" class=\"CitationRef\"\u003e2017\u003c/span\u003e). These elements regulate the opening of plant stomatas, affecting the transpiration and respiration processes, causing, under extreme conditions, a reduction in the rate of CO\u003csub\u003e2\u003c/sub\u003e assimilation and the remobilization of stored carbohydrates to tissues of greater demand, affecting the development and plant production (Silva et al. \u003cspan citationid=\"CR17\" class=\"CitationRef\"\u003e2020\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eIn this sense, the characterization of climatic conditions and their seasonal occurrence in a given region can be strategies to aid in agricultural planning because it is a tool that allows delimiting regions with favorable climatic conditions for agricultural and non-favorable for the cultivation of plants (Tavares et al. \u003cspan citationid=\"CR20\" class=\"CitationRef\"\u003e2018\u003c/span\u003e; Wang et al. \u003cspan citationid=\"CR25\" class=\"CitationRef\"\u003e2019\u003c/span\u003e). To carry out the climatic classification, the frequently used methods involve the indices of Koppen and Geiger (1928), Thornthwaite (\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e1948\u003c/span\u003e), and Thornthwaite and Mather (\u003cspan citationid=\"CR21\" class=\"CitationRef\"\u003e1955\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eThe method by Thornthwaite and Mather (\u003cspan citationid=\"CR21\" class=\"CitationRef\"\u003e1955\u003c/span\u003e) is considered an efficient system in the characterization of different climatic areas because uses the climatological water balance index (CWB) (Elguindi et al. \u003cspan citationid=\"CR4\" class=\"CitationRef\"\u003e2014\u003c/span\u003e; Rolim and Aparecido \u003cspan citationid=\"CR13\" class=\"CitationRef\"\u003e2015\u003c/span\u003e; Sun et al. \u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e2017\u003c/span\u003e), which makes the method sensitive in the detection of small spatial variations and allows to obtain in a practical and simplified way the storage of water in the soil (Cetin et al. \u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e2020\u003c/span\u003e). Therefore, its use in agriculture is considered adequate because it considers the plant as a physical medium, since it conducts water from the soil to the atmosphere through transport mechanisms, relating the water needs of the crop to the climatic conditions of the region (Rolim et al. \u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e2007\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eStudies of climatic characterization that use the method of Thornthwaite and Mather (\u003cspan citationid=\"CR21\" class=\"CitationRef\"\u003e1955\u003c/span\u003e) are fundamental for the understanding of the regions climate, which allows the expansion of new areas of cultivation and the optimization of the productivity of the cultures. However, these studies for the MATOPIBA region are scarce. Thus, we aimed to characterize the climatic conditions of the MATOPIBA region and its changes in scenarios of climate change using the classification index of Thornthwaite (\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e1948\u003c/span\u003e).\u003c/p\u003e "},{"header":"2. Material And Methods","content":"\u003cdiv id=\"Sec3\" class=\"Section2\"\u003e\n\u003ch2\u003e2.1. Study area and climate dataset\u003c/h2\u003e\n\u003cp\u003eThe study was performed in the MATOPIBA region (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e1\u003c/span\u003e), corresponding to part of the Brazilian Cerrado, with approximately 249,665 km\u0026sup2;, which includes 337 municipalities with approximately 6\u0026nbsp;million inhabitants, of which 2\u0026nbsp;million are residents in the rural area (IBGE \u003cspan class=\"CitationRef\"\u003e2010\u003c/span\u003e). To cover the entire MATOPIBA region, climatic data were collected from 1950 to 1990 for the 467 municipalities in the states of Maranh\u0026atilde;o, Tocantins, Piau\u0026iacute;, and Bahia, inserted in this region. Air temperature data (T, \u0026deg;C) and rainfall (R, mm) were collected in the Meteorological Database for Teaching and Research (MDTR) of the National Institute of Meteorology of Brazil - INMET (Brazil 1992).\u003c/p\u003e\n\u003ch2\u003e2.2. Reference evapotranspiration and climatological water balance\u003c/h2\u003e\n\u003cp\u003eThe reference evapotranspiration (ETo) was calculated using the method of Thornthwaite (\u003cspan class=\"CitationRef\"\u003e1948\u003c/span\u003e), following equations \u003cspan class=\"InternalRef\"\u003e1\u003c/span\u003e\u0026ndash;\u003cspan class=\"InternalRef\"\u003e6\u003c/span\u003e.\u003c/p\u003e\n\u003cdiv id=\"Equ1\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ1\" class=\"mathdisplay\"\u003e$${ET}_{p}=-415.85+23.24T-0.43{T}^{2} for T\\ge 26.5 \\text{℃}$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e1\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ2\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ2\" class=\"mathdisplay\"\u003e$${\\text{E}\\text{T}}_{\\text{p}}=16{\\left(\\frac{10\\text{T}}{\\text{I}}\\right)}^{\\text{a}} \\text{f}\\text{o}\\text{r} 0 \\text{℃}\\le \\text{T}cript\u0026gt;$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e2\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ3\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ3\" class=\"mathdisplay\"\u003e$$I={\\left(0.2\\times Ta\\right)}^{1.514}$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e3\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ4\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ4\" class=\"mathdisplay\"\u003e$$a=0.4924+1.79\\times {10}^{-2} I-7.71\\times {10}^{-5} {I}^{2}+6.75\\times {10}^{-7}{I}^{3}$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e4\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ5\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ5\" class=\"mathdisplay\"\u003e$$Cor=\\left(\\frac{ND}{30}\\right)\\times \\left(\\frac{N}{12}\\right)$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e5\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ6\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ6\" class=\"mathdisplay\"\u003e$$ETo={ET}_{p}\\times Cor$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e6\u003c/div\u003e\n\u003c/div\u003e\n\u003cp\u003ewhere ET\u003csub\u003ep\u003c/sub\u003e is the standard 30-day evapotranspiration (mm 30 days\u003csup\u003e-1\u003c/sup\u003e); N is photoperiod in hours; I and a are thermal indices; T is the average temperature for a given day or period (\u0026deg;C); Ta is the climatological normal annual temperature (\u0026deg;C); Cor is the correction factor; ND is the number of days, and ETo is reference evapotranspiration (mm day\u003csup\u003e-1\u003c/sup\u003e).\u003c/p\u003e\n\u003cp\u003eThe climatological water balance (CWB) was estimated for all studied locations, according to the methodology established by Thornthwaite and Mather (1955) (Fig. 2). The maximum available water capacity in the soil of 100 mm was used as a parameter, commonly used, for the purposes of regional climatic characterization (Carvalho et al. 2010; Rodrigues et al. 2018).\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec4\" class=\"Section2\"\u003e\n\u003ch2\u003e2.3. Classification of Thornthwaite (\u003cspan class=\"CitationRef\"\u003e1948\u003c/span\u003e)\u003c/h2\u003e\n\u003cp\u003eIn the climate classification system of Thornthwaite (1948), reference values were used for the CWB extract, using the annual surplus (SUR year), annual water deficiency (DEF annual) and annual evapotranspiration (PET year) in millimeters (mm year\u003csup\u003e-1\u003c/sup\u003e). These combined variables resulted in the four criteria used for classification (Fig. 3).\u003c/p\u003e\n\u003cp\u003eThe first criterion corresponds to the adequacy of humidity (first letter of classification) responsible for determining the nine major climatic types, obtained by calculating the water index (Im, %), indicating the relationship between excess water and water need. The second criterion (second letter of classification) represents the seasonal distribution of humidity, determining the climatic subclass of the region, for the water factor, through the aridity index equation (Ia, %) that relates the water deficit and water need and humidity (Ih). Equations 7 at 9 were used to obtain water (Im), aridity (Ia) and humidity (Ih) indices.\u003c/p\u003e\n\u003cdiv id=\"Equ7\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ7\" class=\"mathdisplay\"\u003e$$\\text{I}\\text{m}=\\text{I}\\text{h}-0.6 \\times \\text{I}\\text{a}$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e7\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ8\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ8\" class=\"mathdisplay\"\u003e$$\\text{I}\\text{a}=\\left(\\frac{DEF yeaar}{ETP year}\\right)\\times 100$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e8\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Equ9\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ9\" class=\"mathdisplay\"\u003e$$\\text{I}\\text{h}=\\left(\\frac{SUT year}{PET year}\\right)\\times 1$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e9\u003c/div\u003e\n\u003c/div\u003e\n\u003cp\u003eThe adequacy of the second class was performed according with water deficit (DEFwinter, DEFsummer) and water surplus (SURwinter, SURsummer) for the seasons summer (⅓DEC + JAN + FEB + ⅔MAR) and winter (⅔JUN + JUL + AUG + ⅔SEP).\u003c/p\u003e\n\u003cp\u003eO terceiro e o quarto crit\u0026eacute;rio foram respons\u0026aacute;veis por adequar os valores de caracter\u0026iacute;sticas termais da regi\u0026atilde;o. Para isso, utilizou-se do c\u0026aacute;lculo da efici\u0026ecirc;ncia t\u0026eacute;rmica que relaciona a evapotranspira\u0026ccedil;\u0026atilde;o potencial anual (PETyear) e concentra\u0026ccedil;\u0026atilde;o da efici\u0026ecirc;ncia t\u0026eacute;rmica no ver\u0026atilde;o (PETsummer), resultando na evapotranspira\u0026ccedil;\u0026atilde;o potencial no ver\u0026atilde;o (Equation 10).\u003c/p\u003e\n\u003cp\u003eThe third and fourth criteria were responsible for adjusting the values of thermal characteristics of the region. For that, we used the thermal efficiency calculation that relates the potential annual evapotranspiration (PETyear) and concentration of thermal efficiency in summer (PETsummer), resulting in potential evapotranspiration in summer (Equation 10).\u003c/p\u003e\n\u003cdiv id=\"Equ10\" class=\"Equation\"\u003e\n\u003cdiv id=\"FileID_Equ10\" class=\"mathdisplay\"\u003e$$\\text{P}\\text{E}\\text{T}\\text{R}=\\left(\\frac{PETsummer}{PETyear}\\right)\\times 100$$\u003c/div\u003e\n\u003cdiv class=\"EquationNumber\"\u003e10\u003c/div\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec5\" class=\"Section2\"\u003e\n\u003ch2\u003e2.4. Climatic sensitivity\u003c/h2\u003e\n\u003cp\u003eClimatic sensitivity was developed by change the average air temperature (\u0026deg; C), in +\u0026thinsp;1.5\u0026deg;C and \u0026minus;\u0026thinsp;1.5\u0026deg;C, and rainfall (mm), in +\u0026thinsp;30% and \u0026minus;\u0026thinsp;30% (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e4\u003c/span\u003e), according to methodology of Pirttioja et al. (\u003cspan class=\"CitationRef\"\u003e2015\u003c/span\u003e). These values of air temperature and rainfall are future projections reported by IPCC (2014), which make it possible to assess possible changes in future climate and possible impacts on climatic parameters, making it possible to analyze how changes in air temperature and rainfall can influence the climatic classification of the MATOPIBA region.\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec6\" class=\"Section2\"\u003e\n\u003ch2\u003e2.5. Results spatialization\u003c/h2\u003e\n\u003cp\u003eThrough the geographic information system was performed the spatial interpolation of all climatic elements for all locations using Kriging method (Krige 1951), with spherical model, a neighbor and a spatial resolution of 0.25\u0026deg;, and the system of Albers' equivalent conical cartographic projection. With the overlapping of the maps was possible obtain the climatic maps for the classifications of Thornthwaite (\u003cspan class=\"CitationRef\"\u003e1948\u003c/span\u003e). The development of all the analyzes used in the work followed the steps informed in the flowchart in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e.\u003c/p\u003e\n\u003c/div\u003e"},{"header":"3. Results And Discussion","content":"\u003cp\u003eAverage annual air temperatures in the MATOPIBA region vary from 19.8 to 29.1 \u0026ordm;C (Fig.\u0026nbsp;6). June (Jun) and July (Jul) are the months with the lowest air temperature, with values between 20 and 21 \u0026ordm;C in the southern portion of the region, located mainly in the extreme West of the Bahia state, and of 24 at 28 \u0026ordm;C in portion Center-West and Center-North of MATOPIBA (Figs.\u0026nbsp;6F and 6G). Elevated temperatures, above 30 \u0026ordm;C, are frequent between September (Sep), October (Oct), and November (Nov) in the Center-North and Northwest portion of MATOPIBA, where the states of Maranh\u0026atilde;o, Tocantins, and Piau\u0026iacute; are located (Figs.\u0026nbsp;6I, 6J, and 6K). During this period, the occurrence of high temperatures coincides with the higher incidence of solar radiation and lower precipitation, which causes heating of the atmosphere through the emission of long-wave radiation on Earth (Reis et al. 2020). On the other hand, the low temperatures recorded in Jun and Jul can are associated with a lack of precipitation and the consequent reduction in air humidity, which causes less absorption of long wave radiation into the atmosphere at night (Reis et al. 2020).\u003c/p\u003e\n\u003cp\u003eThe average air temperature is an abiotic factor that influences the agricultural activity of MATOPIBA because the plants are grown between October (Oct) and April (Apr), a period with high temperatures, where the plants can suffer stress that result in damage physiological, and less growth affecting, consequently, production. For soybeans, the main crop in the region, high temperatures during the rainy season (sowing season) shorten the crop cycle because the rate of degree-day accumulation is faster (Reis et al. 2020). In this sense, tolerant cultivars adapted to high-temperature conditions can be a strategy to keep crops productive on the MATOPIBA agricultural frontier.\u003c/p\u003e\n\u003cp\u003eIn the MATOPIBA region, the average annual rainfall is 1,502.75 mm distributed mostly (88.75%) between Oct and Apr (Fig.\u0026nbsp;7). The highest rainfall levels occur in the Southwest, especially in the region predominated by Tocantins state, with high levels of rainfall distributed evenly during the rainy season (Oct-Apr), varying substantially only in Apr. High rainfall levels are also registered in the Southern of Maranh\u0026atilde;o and extreme West of Bahia. However, spatial reduction of rainfall indices occurs towards the Northeast region of MATOPIBA, especially in Piau\u0026iacute; state, which has an average annual rainfall of 1,080.93 mm. Between May and September (Sep), the lowest levels of rain are observed, below 170 mm, a fact that shows the irregularity in the spatial distribution of rainfall.\u003c/p\u003e\n\u003cp\u003eRainfall scenario in the MATOPIBA region is modulated by atmospheric systems at different scales, which associated with ecosystem and physiographic factors (as a transition between biomes) strongly influence the intra-seasonal variability of precipitation in the region (Valad\u0026atilde;o et al. 2017; Reis et al. 2020). However, even though the atmospheric systems formed by the equatorial positioning of the Intertropical Convergence Zone (ITCZ) and the South Atlantic Convergence Zone (SACZ) determine the occurrence of rainfall indices (Grimm 2011; Oliveira et al. 2017), the different levels of rainfall between Southwest and Northeast portion of MATOPIBA can be explained by the fact that the Northeast portion is located in transition biome between Cerrado and Caatinga (semiarid), having less influence of atmospheric systems. However, the Southwest portion is located in the transition of Cerrado and Amazon biomes, with about 100% of its surface in an Amazonian environment (Reis et al. 2020), therefore, influenced by atmospheric systems. Thus, the variable accumulation of rainfall in the MATOPIBA sub-regions is influenced by different vegetative configurations (Reis et al. 2020).\u003c/p\u003e\n\u003cp\u003eReal evapotranspiration is related to rainfall regime of the region because its occurrence is associated with the availability of water in the soil-plant system, being the main way to quantify the loss of water present in soil and plant for atmosphere (Milly; Dunne 2016). Thus, evapotranspiration in the MATOPIBA region occurs more intensely only during the rainy season (Oct-May), with average real evapotranspiration of 1,044.49 mm and a greater quantity of evapotranspirated water in the Southwest of MATOPIBA (Fig.\u0026nbsp;8). On the other hand, evapotranspiration values less than 40 mm were recorded between Jun and Sep, mainly in the Central and Northeast regions of MATOPIBA.\u003c/p\u003e\n\u003cp\u003eWater surplus in the soil commonly occurs between November (Nov) and April (Apr) (Fig.\u0026nbsp;9), with a total accumulation of 479.57 mm; in this period, rainfall indices above 100 mm are frequent in MATOPIBA (Fig.\u0026nbsp;7). The largest water surplus (150 at 200 mm) is concentrated in the Northwest of MATOPIBA, specifically in the areas of Tocantins state that concentrate 47.48% of all water surplus. In Jun, July, Aug, Sep, and Oct there is no water surplus in the region due to low rainfall, an event that characterizes this period as dry season in MATOPIBA (Figs.\u0026nbsp;9F, 9G, 9H, 9I, and 9J). May presents a water surplus only in the extreme North of MATOPIBA, located in Maranh\u0026atilde;o, with 48.11% of all annual surplus and an average of 561.32 mm (Fig.\u0026nbsp;9E).\u003c/p\u003e\n\u003cp\u003eThe water deficit is variable during all months of the year (Fig.\u0026nbsp;10). However, its concentration is greater from Jun to Sep and reaches all MATOPIBA territory, with a deficit average of 267.09 mm, corresponding to 74.44% of all annual water deficit (Figs.\u0026nbsp;10F, 10G, 10H, and 10I). Water deficit below 5 mm was found in Jan, Feb, Mar, Apr, Nov, and Dec (Figs.\u0026nbsp;10A, 10B, 10C, 10D, 10K, and 10L), the period in which there are marked volumes of rain. In Oct, the water deficit was zero only in the Southwest of MATOPIBA, represented by Tocantins state; however, in other regions of MATOPIBA, the water deficit can reach 150 mm (Fig.\u0026nbsp;10J).\u003c/p\u003e\n\u003cp\u003eMATOPIBA region presented climatic classification variable with four distinct classes distributed vertically throughout its delimitation (Fig.\u0026nbsp;11). Humid regions (class B1 and B2) were classified in 35.04% of MATOPIBA, with subclasses B1wA\u0026rsquo;a\u0026rsquo; (20%) and B2wA\u0026rsquo;a\u0026rsquo; (6%) more frequent (Fig.\u0026nbsp;13A). Class humid B1 predominated in the South, Central, and North of Tocantins, and occurred in small parts of the territories of Bahia and Maranh\u0026atilde;o; while the class humid B2 classification was represented only in small portions of West of Tocantins.\u003c/p\u003e\n\u003cp\u003eMoist subhumid (C2) was the second class with the greatest extension in MATOPIBA, distributed in 68.71%, 38.34%, 14.21% and 81.65% of th e Maranh\u0026atilde;o, Bahia, Tocantins, and Piau\u0026iacute; area, respectively (Fig.\u0026nbsp;11). In addition, it comprised the subclasses C2sA\u0026rsquo;a\u0026rsquo;, C2w2A\u0026rsquo;a', and C2wA\u0026rsquo;a\u0026rsquo;, with this latter class more frequently in the region (Fig.\u0026nbsp;13A). It highlights that these subclasses delimit the areas where the largest producer of soybeans, corn, cotton, and beans are found (Fig.\u0026nbsp;14), indicating that these classifications have more appropriate climatic conditions for the development and production of crops. Class dry subhumid (C1) represented 12.67% of MATOPIBA, and comprised the subclassifications C1dA\u0026rsquo;a\u0026rsquo;, C1s2A\u0026rsquo;a\u0026rsquo;, C1sA\u0026rsquo;a\u0026rsquo;, and C2rA\u0026rsquo;a\u0026rsquo;, being located in the Southwest portion of Piau\u0026iacute; and part of West of Bahia. Among the subclasses found, C2wA\u0026rsquo;a\u0026rsquo;, B1wA\u0026rsquo;a\u0026rsquo;, and C1sA\u0026rsquo;a\u0026rsquo; showed the highest cumulative frequency (around 42%) (Fig.\u0026nbsp;13A), indicating that the classifications are more comprehensive in MATOPIBA.\u003c/p\u003e\n\u003cp\u003eAir temperature and rainfall volume, in climate change scenarios, altered the climatic characterization of the MATOPIBA region with extinction and/or inclusion of climatic classes (Fig.\u0026nbsp;12). Scenarios with increased air temperature showed a reduction in areas of climate humid (B1), mainly in Tocantins, and expansion of the Moist subhumid (C2) and Dry subhumid (C1) classes from the East for West of MATOPIBA (Figs.\u0026nbsp;12A and 12B). In addition, environments characterized as Semiarid (D) were observed in areas of Southwest Piau\u0026iacute; and West of Bahia, especially when the scenario was +\u0026thinsp;3.0 \u0026ordm;C (Fig.\u0026nbsp;12B).\u003c/p\u003e\n\u003cp\u003eWith increasing air temperature, the most frequent climatic subclasses in MATOPIBA were Das\u0026rsquo;a\u0026rsquo;, DdA\u0026rsquo;a\u0026rsquo;, C1sA\u0026rsquo;a\u0026rsquo;, B1wA\u0026rsquo;a\u0026rsquo;, and C2wA\u0026rsquo;a\u0026rsquo; which presented an accumulative frequency around 76% (Figs.\u0026nbsp;13B and 13C). Although these subclasses occur in both +\u0026thinsp;1.5 \u0026ordm;C and +\u0026thinsp;3.0 \u0026ordm;C scenarios, greater coverage of the classes Moist subhumid (C2wA\u0026rsquo;a\u0026rsquo;), Dry subhumid (C1sA\u0026rsquo;a\u0026rsquo;), and Semiarid (das\u0026rsquo;a\u0026rsquo;) were found in scenarios of greater temperature increase (Figs.\u0026nbsp;12B and 13C). These results show that the increase in air temperature alters the climatic conditions of MATOPIBA, which would cause changes in the vegetative configurations of the region, resulting in changes in the transition of biomes, such as reduction of areas of the Cerrado biome and increase of environments with characteristics of biome Caatinga. In addition, the agricultural activity in the region would be drastically affected by climate change caused by the increase in temperature, resulting in risk climatic for the cultivation of plants, thus compromising the production of crops and the agroeconomic development of MATOPIBA.\u003c/p\u003e\n\u003cp\u003eIn Thornthwaite climatic index, the rainfall regime becomes the most influential parameter to determine the climatic classes. In scenarios with changes of +\u0026thinsp;30% in the rainfall regime, the humid class (B4, B3, B2, and B1) occupied 58.14% of the MATOPIBA region (Fig.\u0026nbsp;12C). However, a greater number of climatic subclasses was found in this scenario, with subclasses C1sA\u0026rsquo;a\u0026rsquo; (Dry subhumid), B2wA\u0026rsquo;a\u0026rsquo; (Humid), B3wA\u0026rsquo;a\u0026rsquo; (Humid), B1wA\u0026rsquo;a\u0026rsquo; (Humid), and C2wA\u0026rsquo;a\u0026rsquo; (Moist subhumid) occurring more frequently (Fig.\u0026nbsp;13D). The greater coverage of humid class in MATOPIBA environments, in addition to characterizing the extent of the Amazon biome, indicates that the climatic conditions presented would allow to expansion of agricultural areas, increase the number of harvests per year and increase crop productivity. Thus, the increase of +\u0026thinsp;30% in the rainfall regime becomes the most promising scenario for agroeconomic development in this region.\u003c/p\u003e\n\u003cp\u003eWhen the scenario is of reduction (-30%) in the rainfall regime, the MATOPIBA region presented the climatic classes Moist subhumid (C2), Dry subhumid (C1), and Semiarid (D), with 40.12% of the area occupied by class C1 (Fig.\u0026nbsp;12D). The number of subclasses determined was lower with an expressive frequency of C1sA\u0026rsquo;a\u0026rsquo;, DdA\u0026rsquo;a\u0026rsquo;, DsA\u0026rsquo;a\u0026rsquo;, and C2wA\u0026rsquo;a\u0026rsquo; (Fig.\u0026nbsp;13E). In this scenario, Semiarid environments expanded to areas which were previously classified as Dry subhumid (Fig.\u0026nbsp;11), in the Center-South portion of Maranh\u0026atilde;o, Southwest Piau\u0026iacute;, and part of West of Bahia. The West region of Tocantins was classified as Moist subhumid, while the Dry subhumid class occupied the Central, North, and South portion of MATOPIBA.\u003c/p\u003e\n\u003cp\u003eIn the scenario of lower rainfall, both the Cerrado biome environments and the transition areas, between Cerrado and Caatinga biomes, can be reduced in the MATOPIBA region; however, areas of the Caatinga biome may increase as the Semiard class expands. In addition, the scenario of reduction in the rainfall regime negatively impacts agricultural activity because with low water availability in the soil the plants reduce their photosynthetic efficiency and, consequently, do not reach their productive potential (Taiz et al. 2017).\u003c/p\u003e\n\u003cp\u003eProductive areas located in environments of transition between biomes require technological efforts that encourage an increase in crop production (Ara\u0026uacute;jo et al. 2019), because, in a transition environment between different biomes, ecosystems and climatic conditions are highly diversified, making these areas particularly vulnerable to climate change (Silva et al. 2016). In this sense, areas of MATOPIBA with high production of soy, corn, cotton, and beans would have a strong impact of climate change, since they are located largely in environments of transition from the Cerrado and Caatinga biomes (Fig.\u0026nbsp;14).\u003c/p\u003e\n\u003cp\u003eRegions of the extreme West of Bahia, South of Maranh\u0026atilde;o, and Southwest of Piau\u0026iacute; present the largest productions of soy, corn, cotton, and beans (Fig.\u0026nbsp;14), being environments classified as Moist subhumid climate. However, in climate change scenarios with increased temperatures and reduced rainfall, these regions suffer changes in climatic conditions, with transition of climate classes between Moist subhumid, Dry subhumid, and Semiarid (Figs.\u0026nbsp;12B and 12D).\u003c/p\u003e\n\u003cp\u003eIn the perspective of climate change, studies by Zilli et al. (2020) suggest a reduction in crop production, such as soybeans and corn, in areas of the Cerrado biome, mainly in the MATOPIBA region, with the displacement of productive areas to subtropical regions of the Atlantic Forest. However, part of the impact of climate change on MATOPIBA could be offset by increased productivity, which would maintain the agricultural scenario of region. Thus, efforts are required to invest in technology and changes in management processes, such as adapting the sowing schedule for crops, using drought-resistant cultivars, using irrigation, efficiency in crop fertilization, improving structural and soil conditions, soil fertility, and precision agriculture (Zilli et al. 2020). Therefore, following these strategies makes it possible to adapt the crops to the climatic conditions of the region and may increase or maintain the productive potential of the crops, alleviating the impacts caused by climate change.\u003c/p\u003e"},{"header":"4. Conclusions","content":" \u003cp\u003eMATOPIBA region has air temperature, rainfall and real evapotranspiration averages of 26.28\u0026deg;C, 1,502.75 mm, and 1,044.49 mm, respectively, with the rainy seasons, between October and April, and drought, from May to September, well defined. In addition, this region is characterized by a humid climate (B1 and B2), dry subhumid (C1), and Moist subhumid (C2). However, in climate change scenarios, climatic extreme indices tend to change the pattern, frequency, and distribution of climate class, which can result in increased climate risk conditions for agricultural activity in the MATOPIBA region, generating negative socioeconomic impacts. Therefore, the results obtained can be used to develop strategies to mitigate the vulnerability of crops to climate change conditions.\u003c/p\u003e "},{"header":"Declarations","content":"\u003cp\u003e\u003cstrong\u003eCompliance with ethical standards\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConflict of interest\u003c/strong\u003e The authors declare that they have no conflict of interest.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eFunding Statement:\u003c/strong\u003e This study was financed in part by the IFSULDEMINAS Campus Muzambinho.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAvailability of data and material:\u003c/strong\u003e The data/ material is opened\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCode availability:\u003c/strong\u003e The software used was python and scripts are available\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEthics approval:\u003c/strong\u003e It is not necessary\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConsent to participate:\u003c/strong\u003e All authors approved\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConsent for publication:\u003c/strong\u003e All authors approved\u003c/p\u003e"},{"header":"References","content":"\u003cp\u003eAcompanhamento de safra brasileira de gr\u0026atilde;os. CONAB (2020). v. 7 Safra 2019/20 - Quarto levantamento, Bras\u0026iacute;lia, p. 1-104.\u003c/p\u003e\n\u003cp\u003eAra\u0026uacute;jo MLS, Sano EE, Bolfe \u0026Eacute;L, Santos JRNJ, Santos JS, Silva FB (2019) Spatiotemporal dynamics of soybean crop in the MATOPIBA region, Brazil (1990-2015). Land Use Policy 80: 57-67. \u003ca href=\"https://doi.org/10.1016/j.landusepol.2018.09.040\"\u003ehttps://doi.org/10.1016/j.landusepol.2018.09.040\u003c/a\u003e.\u003c/p\u003e\n\u003cp\u003eElguindi N, Grundstein A, Bernardes S, Turuncoglu U, Feddema J (2014)Assessment of CMIP5 global model simulations and climate change projections for the 21\u003cem\u003e\u003csup\u003est\u003c/sup\u003e\u003c/em\u003e\u0026nbsp;century using a modified Thornthwaite climate classification.\u0026nbsp;Climatic Change 122:\u0026nbsp;523-538.\u0026nbsp;https://doi.org/10.1007/s10584-013-1020-0\u003c/p\u003e\n\u003cp\u003eGrimm AM (2011) Interannual climate variability in South America: impacts on seasonal precipitation, extreme events and possible effects of climate change. Stochastic Environmental Research and Risk Assessment 25(4): 537\u0026ndash;554.\u003c/p\u003e\n\u003cp\u003eHalder D, Kheroar S, Srivastava RK, Panda RK (2020) Assessment of future climate variability and potential adaptation strategies on yield of peanut and Kharif rice in eastern India. Theoretical and Applied Climatology 140: 823-838. https://10.1007/s00704-020-03123-5\u003c/p\u003e\n\u003cp\u003eIBGE. (2010) Censo. Rio de Janeiro. Dispon\u0026iacute;vel em: http://censo2010.ibge.gov.br/ Acesso em: 1 jun. 2020.\u003c/p\u003e\n\u003cp\u003eMilly P, Dunne K (2016) Potential evapotranspiration and continental drying. Nature Climate Change 6: 946\u0026ndash;949.\u003c/p\u003e\n\u003cp\u003eOliveira PT, Silva CMS, Lima KC (2017) Climatology and trend analysis of extreme precipitation in subregions of Northeast Brazil. Theoretical and Applied Climatology 130(1-2): 77\u0026ndash;90.\u003c/p\u003e\n\u003cp\u003ePirttioja N, Carter TR, Fronzek S, Bindi M, Hoffmann H, Palosuo T, Ruiz-Ramos M, Tao R, Trnka M, Acutis M, Asseng S, Baranowiski P, Basso B, Bodin P, Buis S, Cammarano D, Deligios P, Destain M-F, Dumont B, Ewert F, Ferrise R, Fran\u0026ccedil;ois L, Gaiser T, Hlavinka P, Jacquemin I, Kersebaum KC, Kollas C, Krzyszczak J, Lorite IJ, Minet J, Minguez MI, Montesino M, Moriondo M, M\u0026uuml;ller C, Nendel C, \u0026Ouml;zt\u0026uuml;rk I, Perego A, Rodr\u0026iacute;guez A, Ruane AC, Ruget F, Sanna M, Semenov MA, Slawinski C, Stratonovitch P, Supit, Waha K, Wang E, Wu L, Zhao Z, R\u0026ouml;tter RP (2015) Temperature and precipitation effects on wheat yield across a European transect: a crop model ensemble analysis using impact response surfaces. Climate Research 65: 87-105.\u003c/p\u003e\n\u003cp\u003eRausch LL,\u0026nbsp;Gibbs HK,\u0026nbsp;Schelly I, Brand\u0026atilde;o Junior A, Morton DC, Carneiro Filho A, Strassburg B, Walker N, Noojipady P, Barreto P, Meyer D (2019)\u0026nbsp;Soy expansion in Brazil's Cerrado.\u0026nbsp;Conservation Letters 12(6): e12671.\u0026nbsp;https://doi.org/10.1111/conl.12671\u003c/p\u003e\n\u003cp\u003eReis LC, Silva CMS, Bezerra BG, Mutti PR, Spyrides MHC, Silva PE (2020) Analysis of Climate Extreme Indices in the MATOPIBA Region, Brazil. Pure and Applied Geophysics 177: 4457-4478. https://doi.org/10.1007/s00024-020-02474-4.\u003c/p\u003e\n\u003cp\u003eRolim GS, Camargo MBP, Lania DG, Moraes JFL (2007) Classifica\u0026ccedil;\u0026atilde;o clim\u0026aacute;tica de K\u0026ouml;ppen e de Thornthwaite e sua aplicabilidade na determina\u0026ccedil;\u0026atilde;o de zonas agroclim\u0026aacute;ticas para o estado de S\u0026atilde;o Paulo. Revista Bragantia 66(4): 711-720.\u003c/p\u003e\n\u003cp\u003eSilva FB, Santos JRN, Feitosa FECS, Silva IDC, Ara\u0026uacute;jo MLS, Guterres CE, Santos JS, Ribeiro CV, Bezerra DS, Neres RL (2016) Evid\u0026ecirc;ncias de mudan\u0026ccedil;as clim\u0026aacute;ticas na regi\u0026atilde;o de transi\u0026ccedil;\u0026atilde;o Amaz\u0026ocirc;nia-Cerrado no estado do Maranh\u0026atilde;o. Revista Brasileira de Meteorologia 31: 330\u0026ndash;336.\u003c/p\u003e\n\u003cp\u003eSilva JA, Santos PAB, Carvalho LG, Moura EG, Andrade FR (2020) Gas exchanges and growth of soybean cultivars submitted to water deficiency.\u0026nbsp;Pesquisa Agropecu\u0026aacute;ria Tropical\u0026nbsp;50: e58854.\u003c/p\u003e\n\u003cp\u003eSilva VPR, Silva ERA, Maciel GF, Souza EP, Braga CC, Holanda RM (2020) Soybean yield in the MATOPIBA region under climate changes.\u0026nbsp;Revista Brasileira de Engenharia Agr\u0026iacute;cola e Ambiental 24(1): 8-14. https://doi.org/10.1590/1807-1929/agriambi.v24n1p8-14\u003c/p\u003e\n\u003cp\u003eSun X, Li J, Zhou A (2017) Evaluation and comparison of methods for calculating Thornthwaite moisture index. Australian Geomechanics 52(2): 61-75.\u003c/p\u003e\n\u003cp\u003eTaiz L, Zeiger E, M\u0026oslash;ller IM, Murphy A (2017) Fisiologia e desenvolvimento vegetal. Artmed Editora.\u003c/p\u003e\n\u003cp\u003eThornthwaite CW, Mather JR (1955) The water balance. Centerton: Drexel Institute of Technology. Laboratory of Climatology 8(1): 104.\u003c/p\u003e\n\u003cp\u003eThornthwaite CW (1948) An approach toward a rational classification of climate. Geographical review 38(1): 55-94.\u003c/p\u003e\n\u003cp\u003eValad\u0026atilde;o CEA, Carvalho LMV, Lucio PS, Chaves RR (2017) Impacts of the madden-Julian oscillation on Intraseasonal precipitation over Northeast Brazil. International Journal of Climatology 37: 1859\u0026ndash;1884.\u003c/p\u003e\n\u003cp\u003eVendrame PRS, Brito OR, Martins ES, Quantin C, Guimaraes MF, Becquer T (2013) Acidity control in latosols under long-term pastures in the Cerrado region, Brazil. Soil Research 51: 253\u0026ndash;261. https://doi. org/10.1071/sr12214\u003c/p\u003e\n\u003cp\u003eWang C, Linderholm HW, Song Y, Wang F, Liu Y, Tian J, Xu J, Song Y, Ren G (2020) Impacts of drought on maize and soybean production in northeast china during the past five decades.\u0026nbsp;\u003cem\u003eInternational Journal of Environmental Research\u003c/em\u003e\u0026nbsp;and\u0026nbsp;\u003cem\u003ePublic Health\u003c/em\u003e 17: 2459.\u003c/p\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":true,"hideJournal":true,"highlight":"","institution":"","isAcceptedByJournal":false,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"
[email protected]","identity":"researchsquare","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":true,"externalIdentity":"","sideBox":"","snPcode":"","submissionUrl":"/submission","title":"Research Square","twitterHandle":"researchsquare","acdcEnabled":true,"dfaEnabled":false,"editorialSystem":"","reportingPortfolio":"","inReviewEnabled":false,"inReviewRevisionsEnabled":true},"keywords":"Temperature, rainfall, climate variability, climate extreme index, northeast of Brazil","lastPublishedDoi":"10.21203/rs.3.rs-428799/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-428799/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003eIdentify the climatic characterization of a region and its spatial and temporal variation, as well as its changes in the face of climate change events, is essential for agrometeorological studies because they can assist in the planning of strategies that reduce the negative impacts generated in the cultures exposed to critical climatic conditions. Thus, this study aimed to characterize the climatic conditions of the MATOPIBA region and its changes in scenarios of climate change using the classification index of Thornthwaite (\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e1948\u003c/span\u003e). Daily time series of rainfall and temperature data in the 1950\u0026ndash;1990 period were used, arranged in a 0.25\u0026ordm; \u0026times; 0.25\u0026ordm; grid, covering 467 points over the studied region. The data set was used to estimate climatological water balance and climate index Thornthwaite (\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e1948\u003c/span\u003e), and obtain the trends climatological according to IPCC (2014) climate change projections, with changes in the average air temperature (+\u0026thinsp;1.5\u0026deg;C and \u0026minus;\u0026thinsp;1.5\u0026deg;C) and precipitation (+\u0026thinsp;30% and \u0026minus;\u0026thinsp;30%). The MATOPIBA region is characterized by its humid, dry subhumid, and Moist subhumid climate, with the rainy seasons, between October and April, and drought, from May to September, well defined. In MATOPIBA climate change scenarios, climatic extreme indices tend to alter the pattern, frequency, and distribution of climate class, which can increase climate risk and impact crop production. Therefore, the results obtained can be used to develop strategies to mitigate the vulnerability of crops to climate change conditions.\u003c/p\u003e","manuscriptTitle":"Climate change in MATOPIBA region of Brazil using Thornthwaite (1948) classification","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2021-04-19 22:22:57","doi":"10.21203/rs.3.rs-428799/v1","editorialEvents":[{"type":"communityComments","content":0}],"status":"published","journal":{"display":true,"email":"
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