Progress and opportunities for monitoring greenhouse gases fluxes in Mexican ecosystems: the MexFlux network

Progress and opportunities for monitoring greenhouse gases fluxes in Mexican ecosystems: the MexFlux network

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Corresponding author: R. Vargas; e-mail: [email protected] Received March 15, 2012; accepted September 4, 2012 RESUMEN Para entender los procesos de los ecosistemas desde un punto de vista funcional es fundamental entender las UHODFLRQHVHQWUHODYDULDELOLGDGFOLPiWLFDORVFLFORVELRJHRTXtPLFRV\ODVLQWHUDFFLRQHVVXSHU¿FLHDWPyVIHUD (QODV~OWLPDVGpFDGDVVHKDDSOLFDGRGHPDQHUDFUHFLHQWHHOPpWRGRGHFRYDULDQ]DGHÀXMRVWXUEXOHQWRV (& SRUVXVVLJODVHQLQJOpV HQHFRVLVWHPDVWHUUHVWUHVPDULQRV\XUEDQRVSDUDPHGLUORVÀXMRVGHJDVHVGHLQYHUQDGHUR SHM&22, H22 \HQHUJtD SHMFDORUVHQVLEOH\ODWHQWH (QGLYHUVDVUHJLRQHVVHKDQHVWDEOHFLGR UHGHVGHVLVWHPDV(&TXHKDQDSRUWDGRLQIRUPDFLyQFLHQWt¿FDSDUDHOGLVHxRGHSROtWLFDVDPELHQWDOHV\GH DGDSWDFLyQ(QHVWHFRQWH[WRHOSUHVHQWHWUDEDMRGHOLPLWDHOPDUFRFRQFHSWXDO\WpFQLFRSDUDHOHVWDEOHFLPLHQWR GHXQDUHGUHJLRQDOGHPHGLFLyQGHÀXMRVGHJDVHVGHHIHFWRLQYHUQDGHURHQ0p[LFRGHQRPLQDGD0H[)OX[ FX\RREMHWLYRSULQFLSDOHVPHMRUDUQXHVWUDFRPSUHQVLyQGHODIRUPDHQTXHODYDULDELOLGDGFOLPiWLFD\OD WUDQVIRUPDFLyQDPELHQWDOLQÀX\HHQODGLQiPLFDGHORVHFRVLVWHPDVPH[LFDQRVDQWHORVIDFWRUHVGHFDPELR ambiental global. En este documento se analiza primero la importancia del intercambio de CO2 y vapor de DJXDHQWUHORVHFRVLVWHPDVWHUUHVWUHV\ODDWPyVIHUD'HVSXpVVHGHVFULEHEUHYHPHQWHODWpFQLFDGHFRYDULDQ]D GHÀXMRVWXUEXOHQWRVSDUDODPHGLFLyQGHpVWRV\VHSUHVHQWDQHMHPSORVGHPHGLFLRQHVHQGRVHFRVLVWHPDV WHUUHVWUHV\XQRXUEDQRHQ0p[LFR3RU~OWLPRVHGHVFULEHQODVEDVHVFRQFHSWXDOHV\RSHUDWLYDVDFRUWR PHGLDQR\ODUJRSOD]RSDUDODFRQWLQXLGDGGHODUHG0H[)OX[

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ABSTRACT Understanding ecosystem processes from a functional point of view is essential to study relationships among climate variability, biogeochemical cycles, and surface-atmosphere interactions. Increasingly during the last GHFDGHVWKHHGG\FRYDULDQFH (& PHWKRGKDVEHHQDSSOLHGLQWHUUHVWULDOPDULQHDQGXUEDQHFRV\VWHPVWR TXDQWLI\ÀX[HVRIJUHHQKRXVHJDVHV HJ, CO2, H22 DQGHQHUJ\ HJ, sensible and latent heat). Networks of (&V\VWHPVKDYHEHHQHVWDEOLVKHGLQGLIIHUHQWUHJLRQVDQGKDYHSURYLGHGVFLHQWL¿FLQIRUPDWLRQWKDWKDVEHHQ XVHGIRUGHVLJQLQJHQYLURQPHQWDODQGDGDSWDWLRQSROLFLHV,QWKLVFRQWH[WWKLVDUWLFOHRXWOLQHVWKHFRQFHSWXDO DQGWHFKQLFDOIUDPHZRUNIRUWKHHVWDEOLVKPHQWRIDQ(&UHJLRQDOQHWZRUN LH0H[)OX[ WRPHDVXUHWKH VXUIDFHDWPRVSKHUHH[FKDQJHRIKHDWDQGJUHHQKRXVHJDVHVLQ0H[LFR7KHJRDORIWKHQHWZRUNLVWRLPSURYH RXUXQGHUVWDQGLQJRIKRZFOLPDWHYDULDELOLW\DQGHQYLURQPHQWDOFKDQJHLQÀXHQFHWKHG\QDPLFVRI0H[LFDQ ecosystems. First, we discuss the relevance of CO2DQGZDWHUYDSRUH[FKDQJHEHWZHHQWHUUHVWULDOHFRV\VWHPVDQGWKHDWPRVSKHUH6HFRQGZHEULHÀ\GHVFULEHWKH(&EDVLVDQGSUHVHQWH[DPSOHVRIPHDVXUHPHQWV LQWHUUHVWULDODQGXUEDQHFRV\VWHPVRI0H[LFR)LQDOO\ZHGHVFULEHWKHFRQFHSWXDODQGRSHUDWLRQDOJRDOVDW VKRUWPHGLXPDQGORQJWHUPVFDOHVIRUFRQWLQXLW\RIWKH0H[)OX[QHWZRUN .H\ZRUGV: Environmental networks, eddy covariance, FLUXNET, greenhouse gases, long-term measurePHQWVVXUIDFHDLUH[FKDQJH

1. ,QWURGXFWLRQ Humankind faces new challenges to develop policies for the reduction, adaptation and mitigation of JOREDOHQYLURQPHQWDOFKDQJH7KHVFLHQWL¿FFRPmunity has the responsibility of providing information to enable the development of such policies and strategies. This includes the generation of knowledge about the components, processes and mechanisms by ZKLFKHFRV\VWHPVUHVSRQGWR  FOLPDWHYDULDELOLW\ DQG  WKHLQWHUDFWLRQDQGHIIHFWVRIJUHHQKRXVHJDVHV HJ, CO2, CH4, N2O) on global climate. From a functional standpoint, the interaction between climate variability, vegetation dynamics HJ, land use change), and biogeochemical cycles are necessary to understand ecosystem processes ZLWKLQWKHFRQWH[WRIJOREDOHQYLURQPHQWDOFKDQJH &KDSLQHWDO, 2002). From a socio-ecological point of view, the water and carbon cycles are critical for the regulation and supporting of ecosystem services, and therefore represent part of our natural capital 0LOOHQQLXP (FRV\VWHP$VVHVVPHQW   7KXV LWLVLPSRUWDQWWR  HYDOXDWHWKHLQÀXHQFHRIWKHVH SURFHVVHV RQ DWPRVSKHULF G\QDPLFV   HVWLPDWH the potential ecosystem services provided to human SRSXODWLRQVDQG  SURYLGHUHOHYDQWLQIRUPDWLRQWR GH¿QHSROLFLHVIRUPDQDJHPHQWDQGFRQVHUYDWLRQ Through the processes of photosynthesis and respiration, ecosystems play a key role in the capture and emission of CO2 )LJ )XUWKHUPRUHWKHFKDUacteristics of vegetation cover also affect water vapor ÀX[HVLQWRWKHDWPRVSKHUHWKURXJKHYDSRWUDQVSLUDWLRQ )LJ DQGWKHUHIRUHWKHEDODQFHEHWZHHQVHQVLEOH

DQG ODWHQW KHDW ÀX[HV WKDW LPSDFW WKH DWPRVSKHUH )LVKHUHWDO $GGLWLRQDOO\WKHW\SHDQGH[WHQW RIYHJHWDWLRQGH¿QHVWKHSK\VLFDOSURSHUWLHVVXFKDV surface albedo, emissivity and aerodynamic roughness that can affect air temperature, precipitation, and wind VSHHG %XUEDDQG9HUPD ,QWXUQFOLPDWHLVWKH main factor determining the presence and distribution of ecosystems around the world, and establishes FRPSOH[IHHGEDFNVEHWZHHQWKHELRVSKHUHDQGJOREDO ELRJHRFKHPLFDOF\FOHV %RQDQ+HLPDQQDQG Reichstein, 2008). Current knowledge on the interactions between climate and carbon and water cycles is still limited. 7KLV KDV EHHQ LGHQWL¿HG E\ WKH ,QWHUJRYHUQPHQWDO 3DQHORQ&OLPDWH&KDQJH ,3&& DVD³NH\XQFHUWDLQty” in our understanding of present and future climate ,3&&   7KH H[SHULPHQWDO HYDOXDWLRQ RI WKH interaction between weather and these cycles has PDGHVLJQL¿FDQWSURJUHVVZLWKWKHGHYHORSPHQWRI QHZPHWKRGRORJLHVWRPHDVXUHWKHPDVV HJ, water vapor, CO2  DQG HQHUJ\ H[FKDQJH HJ, sensible heat, solar radiation) at multiple spatial and temporal VFDOHV &DQDGHOOHWDO, 2000). This development has required a multidisciplinary link between earth and atmospheric sciences, functional ecology, biogeochemistry, and mathematics, which has improved WKHDSSOLFDWLRQRIPRGHOGDWDIXVLRQ 9DUJDVHWDO, D 7KLVVFLHQWL¿FGHYHORSPHQWNQRZQDVWKH WKLUG VFLHQWL¿F SDUDGLJP LV FRPSOHPHQWHG E\ WKH integration of knowledge from computer systems science, which is emerging as the fourth paradigm LQVFLHQWL¿FUHVHDUFK +H\HWDO, 2009).

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During the last decades, several networks for monitoring ecosystem processes and attributes KDYH EHHQ HVWDEOLVKHG HJ, International Long Term Ecological Research Network, [ILTER], and Human and Biophysical Dimensions of Tropical Dry Forests in the Americas [Tropi-Dry], among RWKHUV 7KHVHQHWZRUNVKDYHVWDQGDUGL]HGH[SHULmental protocols, which have allowed collecting a large amount of information and created regional V\QWKHVLVUHSRUWV *UHHQODQGHWDO, 2003). Another H[DPSOH LV )/8;1(7²WKH JOREDO QHWZRUN IRU ÀX[PHDVXUHPHQWVRIZDWHUYDSRU&22, and energy LQWHUUHVWULDOHFRV\VWHPV %DOGRFFKLet al., 2001). This network incorporates more than 500 study sites around the world, which have been used for the analysis of ecosystem primary productivity, evapotranspiration, and the response of ecosystems WR GLVWXUEDQFHV %DOGRFFKL   )/8;1(7 LV considered a network of networks that consists RI VHYHUDO UHJLRQDO QHWZRUNV HJ$PHUL)OX[ LQ the United States of America, CarboEurope in Europe). Despite its broad coverage, FLUXNET sites are mainly located in temperate ecosystems, with annual temperatures between 5 and 17 ºC, annual rainfall between 600 and 1250 mm, and latitudes above 30 ºN.

Similarly, in recent years new sites for monitoring CO2DQGHQHUJ\ÀX[HVWRWKHDWPRVSKHUHKDYHEHHQ HVWDEOLVKHG DW YDULRXV XUEDQ ORFDWLRQV LH, Urban )OX[1HWZRUN 7KHQXPEHURIVLWHVLQWKLVQHWZRUN is still much lower than those for FLUXNET with ~30 sites of which only 20 are active and only two correspond to sub-tropical cities. Importantly, more than 70% of CO2 emissions of anthropogenic origin occurs in cities, despite occupying only 2% of the WRWDOODQGDUHD /H4XpUpet al., 2009). The time is ripe for the establishment of a 0H[LFDQ HGG\ FRYDULDQFH (&  QHWZRUN IRU VHYeral reasons. First, long-term impact of land use change and anthropogenic changes in biogeography have fragmented and fundamentally transformed 0H[LFDQ ODQGVFDSHV 7KHVH WUDQVIRUPDWLRQV KDYH created a highly heterogeneous vegetation cover IRUPLQJFRPSOH[ODQGVFDSHPRVDLFVWKDWGLIIHULQ plant cover, age, plant species, and functional group composition over a wide range of spatial scales 0LWWHUPHLHU DQG *RHWWVFK   6HFRQG DULG semiarid and tropical ecosystems are underrepreVHQWHGLQ)/8;1(7 %DOGRFFKL 7KLVLVRI SDUWLFXODUUHOHYDQFHIRU0H[LFREHFDXVHRYHU of its territory is represented by arid and semiarid HFRV\VWHPVORFDWHGEHORZWKHž1ODWLWXGH &KDO-

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SURYLGHWKHVFLHQWL¿FEDVLVIRUSXEOLFSROLF\WRUHGXFH HPLVVLRQV DGDSWDWLRQPLWLJDWLRQ WR HQYLURQPHQWDO change and early detection of environmental hazards HJ ORVV RI KDELWDWELRGLYHUVLW\ H[WUHPH ZHDWKHU events). This manuscript addresses the following LVVXHV  GHVFULSWLRQRI&22DQGZDWHUYDSRUÀX[HV IURP WHUUHVWULDO HFRV\VWHPV   WKH (& WHFKQLTXH IRUPHDVXULQJWKHVHÀX[HVDQG  WKHFRQFHSWXDO and operational goals at short-, medium- and longWHUPVFDOHVIRUSHUPDQHQWRSHUDWLRQRIWKH0H[)OX[ network. 2. 0DLQ &22 DQG ZDWHU YDSRU ÀX[HV LQ WHUUHVWULDO HFRV\VWHPV 7KHPDLQFDUERQÀX[HVFRQVLVWHVVHQWLDOO\RIJDLQV and losses of CO2 LQ HFRV\VWHPV &KDSLQ HW DO,   )LJ 7KHWRWDODPRXQWRIFDUERQLQFRUporated into the ecosystem through photosynthesis LVNQRZQDVJURVVSULPDU\SURGXFWLRQ *33 DQG it is estimated that the global GPP average is about 123 PgCyr–1 %HHUHWDO, 2010). A proportion of CO2

7DEOH,,6SHFL¿FREMHFWLYHVIRUWKH0H[)OX[QHWZRUN 1. 7RTXDQWLI\WKHVSDWLDODQGWHPSRUDOYDULDWLRQRIFDUERQVWRUDJHDQGH[FKDQJHRIJUHHQKRXVHJDVHVDQGHQHUJ\LQ WKHPDLQWHUUHVWULDOFRDVWDOPDULQHDQGXUEDQHFRV\VWHPVRI0H[LFR 2. To understand the mechanisms that regulate the dynamics of greenhouse gases from ecosystems as well as the ELRJHRFKHPLFDOF\FOHVRIFDUERQZDWHUDQGQLWURJHQWKURXJKREVHUYDWLRQDODQGPDQLSXODWLYHH[SHULPHQWVDQG models of ecosystem processes. 3. 7RXQGHUVWDQGWKHPHFKDQLVPVWKDWFRQWUROWKHHQHUJ\SDUWLWLRQLQJLQUHSUHVHQWDWLYHHFRV\VWHPVRI0H[LFRWKURXJK REVHUYDWLRQVH[SHULPHQWVDQGPRGHOV 4. To build a high quality historical database for site-level analysis, and data-synthesis activities at regional and global scales. 5. To support and guide the individual efforts of new researchers interested in establishing new monitoring sites and PHWKRGVIRUTXDQWLI\LQJFDUERQVWRFNVDQGÀX[HVRIJUHHQKRXVHJDVHVDQGHQHUJ\ 6. To establish standardized protocols for measurements, calibration, data processing, data archiving, and data sharing, in order to provide value added products for research and policymaking.

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captured by ecosystems returns to the atmosphere YLDHFRV\VWHPUHVSLUDWLRQ 5HFR 7KHEDODQFHEHtween CO2 captured via GPP and loss through Reco LVWKHQHWHFRV\VWHPH[FKDQJH 1(( ZKLFKXOWLmately determines if the ecosystem is a net carbon VRXUFHRUVLQN )LJ 7KH1((UHSUHVHQWVWKHWRWDO CO2H[FKDQJHGYHUWLFDOO\EHWZHHQODQGVXUIDFHDQG the atmosphere, and can be directly measured using WKHPLFURPHWHRURORJLFDOWHFKQLTXHRI(& $XELQHW HWDO, 2000; Baldocchi, 2003). Furthermore, Reco components include the emission of CO2IURPVRLOV 9DUJDVHWDO, 2011a) known DVWRWDOVRLOUHVSLUDWLRQ 56 DQGWRDOHVVHUH[WHQWE\ autotrophic respiration of leaves and stems of plants 5$S)LJ 56UHVXOWVIURPWKHSURGXFWLRQRI&22 E\KHWHURWURSKLFRUJDQLVPV LH, heterotrophic respiraWLRQ5K DQGDXWRWURSKLFUHVSLUDWLRQ 5$VSURGXFWLRQ of CO2 by plant roots and organisms directly associated ZLWKWKHUKL]RVSKHUH  +DQVRQHWDO, 2000). Although we can identify the components that contribute for the ecosystem carbon balance, methodological uncertainWLHVVWLOOH[LVW)RUH[DPSOHWRGDWHWKHUHLVQRWKHRUHWical model to represent the biophysical mechanisms that regulate the temporal and spatial variation of RS %RQG/DPEHUW\DQG7KRPVRQ9DUJDVHWDO, 2011a). One complication arises from the uncertainty in the estimation of RS as it varies throughout the year 0DKHFKDHWDO, 2010) due to the heterogeneity of the contributions by RAs and Rh under different soil and environmental conditions. (YDSRWUDQVSLUDWLRQ (7  LV WKH VXP RI ZDWHU transferred from the Earth’s surface to the atmosphere WKURXJKHYDSRUDWLRQ (Y DQGSODQWWUDQVSLUDWLRQ 7U )LJ  )LVKHUHWDO, 2011). Evaporation comprises the movement of water into the atmosphere from soil, plant surfaces and water bodies. The transport of water from the surface to the atmosphere through evaporation and transpiration constitutes up to 75% RIWKHWRWDOHQHUJ\WUDQVIHURQWKHSODQHW -XQJHWDO, 2010). These processes are closely related to GPP, since the opening of stomata during photosynthesis is inevitably accompanied by water loss through transpiration, while the residence time of water in the soil largely controls the rate of decomposition RIRUJDQLFPDWWHUDQGFRQVHTXHQWO\56
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3. (GG\ FRYDULDQFH (& WHFKQLTXH 7KHHQHUJ\DQGPDVVH[FKDQJHEHWZHHQWKHELRVSKHUH and atmosphere can be studied through different methods depending on the characteristics of the ecosystem and the spatial and temporal scales RI LQWHUHVW &DQDGHOO HW DO, 2000). At the scale RI H[SHULPHQWDO SORWV LH, square meters), gas H[FKDQJHFKDPEHUVSURYLGHLQIRUPDWLRQRQPLFURELDO and plant ecophysiological processes that control WKH H[FKDQJH RI ZDWHU YDSRU DQG &2 2 9DUJDV HW DO, 2011a). However, the spatial sampling is OLPLWHG PDNLQJ LW GLI¿FXOW WR H[WUDSRODWH UHVXOWV to larger spatial scales, and undesirable effects of FRQ¿QHPHQWDQGPDQLSXODWLRQPD\DOVREHLQKHUHQW WR WKH PHWKRGRORJ\ 3XPSDQHQ HW DO, 2004). For scales between 100 to 1000 m2 ZKLFK DUH PRVW representative of an ecosystem) micrometeorological techniques are a useful approach to monitor HFRV\VWHP H[FKDQJH SURFHVVHV RI ZDWHU YDSRU CO2, other biogenic gases, and aerosols. Among micrometeorological techniques, the EC has been the most widely used for estimating NEE by direct PHDVXUHPHQWRIYHUWLFDOÀX[HVRIPDVVDQGHQHUJ\ DFURVVDKRUL]RQWDOSODQHDERYHWKHFDQRS\ $XELQHW HW DO, 2000; Baldocchi, 2003). This technique is LQ VLWX and non-destructive, and can be applied to time scales ranging from fractions of an hour WR \HDUV LW LV WKHUHIRUH LGHDO WR FDSWXUH WKH ÀX[ dynamics across different weather conditions from diurnal cycles to long-term environmental changes %DOGRFFKL  7KH WHFKQLTXH LV DOVR VXLWDEOH for understanding the response of ecosystems to disturbance, management history and comparative studies between ecosystem functional types, or for GLIIHUHQW VXFFHVVLRQDO VWDJHV %DOGRFFKL   +RZHYHU LWV LPSOHPHQWDWLRQ LV FRPSOH[ EHFDXVH WKHVWXG\VLWHVKRXOGEHLQDUHODWLYHO\ÀDWWHUUDLQ and be homogeneous in terms of vegetation and soil. The installation and operation of instruments, as well as processing and data analysis require special attention for correct results representing the HFRV\VWHP 3DSDOHHWDO, 2006). %ULHÀ\WXUEXOHQWH[FKDQJHVRIPRPHQWXPKHDW water vapor, CO2, and in general any scalar, can be PDWKHPDWLFDOO\ GH¿QHG DV WKH FRYDULDQFH EHWZHHQ WKH LQVWDQWDQHRXV GHYLDWLRQV RU ÀXFWXDWLRQV RI WKH VFDODULQTXHVWLRQ HJ, temperature, concentration of water vapor or CO2 PL[LQJUDWLR DQGYHUWLFDOZLQG YHORFLW\RYHUDVSHFL¿FWLPHLQWHUYDO HJ, 30 min).

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)RU H[DPSOH WKH YHUWLFDO WXUEXOHQW ÀX[ RI &22 is GH¿QHGDVWKHFRYDULDQFHEHWZHHQWKHÀXFWXDWLRQV of vertical wind speed and CO2PDVVGHQVLW\ Z¶F¶) PXOWLSOLHGE\WKHDYHUDJHDLUGHQVLW\ a  %DOGRFFKL   ,I WKH QHW ÀX[ LV SRVLWLYH LH, towards the atmosphere) the ecosystem is a net source, but on the FRQWUDU\LIWKHÀX[LVQHJDWLYHWKHQWKHHFRV\VWHP functions as a sink. 7RPRQLWRUÀX[HVRIJUHHQKRXVHJDVHV *+*V  and energy using this technique, the installation of a micrometeorology tower with particular equipment located at a suitable height is required, to ensure the UHSUHVHQWDWLYHQHVVQHHGHGIRUWKHH[FKDQJHVXUface in all directions. The height and position of the tower in turn depend on the height of the vegetation as well as the predominant wind direction and the average wind speed. A basic EC system to measure ÀX[HVRI&22 consists of a three-dimensional sonic anemometer and a CO2 analytical sensor. Fast-response CO2 analyzers are based on the principle of absorption of infrared radiation by trace gases, and often measure CO2 and water vapor at the same time. Also an EC system includes basic equipment WR PHDVXUH K\GURPHWHRURORJLFDO YDULDEOHV HJ, precipitation, temperature, relative humidity, soil temperature and moisture), and the surface available

HQHUJ\ LHWKHQHWUDGLDWLRQDQGJURXQGKHDWÀX[  Several publications contain detailed descriptions of WKH(&PHWKRGLQWHUUHVWULDOHFRV\VWHPV *RXOGHQet DO, 1996; Aubinet HWDO, 2000; Baldocchi, 2003) and FLWLHV 9HODVFRDQG5RWK  4. 7KH FRQFHSWXDO IUDPHZRUN DQG RSHUDWLRQDO 0H[)OX[ Current knowledge of the dynamics of carbon and ZDWHUÀX[HVLQ0H[LFDQHFRV\VWHPVLVYHU\OLPLWHG 9DUJDVHWDO, 2012a). Among the research published in peer-reviewed literature are RS measurements in WURSLFDOIRUHVWV 'DYLGVRQHWDO, 1993; Vargas and Allen, 2008; Vargas, 2012), NEE from subtropical DQG VHPLDULG HFRV\VWHPV +DVWLQJV HW DO, 2005; Pérez-Ruiz HWDO DQGLQXUEDQDUHDVRI0H[LFR &LW\ 9HODVFRHWDO, 2005, 2009, 2011), and ET in VHPLDULGHFRV\VWHPV :DWWVHWDO, 2007; Vivoni HWDO, 2008). These measurements of energy, water vapor and CO2 ÀX[HV LQ 0H[LFDQ HFRV\VWHPV RULJLQDWHG from individual efforts, and unfortunately there is a lack of a strategic governmental program to ensure long-term funds for the establishment and continuity of these types of studies. 0H[)OX[ LV WKH QHWZRUN RI ÀX[ PHDVXUHPHQWV RI*+*VDQGHQHUJ\ÀX[HVIURPWHUUHVWULDOXUEDQ

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intended to grow in coming years, as new sites will be established within strategic ecosystems to ensure the long-term operation of the network. The new sites, in addition to consistency with the assumptions for EC technique, should ideally be located at sites WKDWUHSUHVHQWWKHYDULDELOLW\RI0H[LFDQHFRV\VWHPV DQGRUDWHFRV\VWHPVDQGUHJLRQVPRVWYXOQHUDEOHWR environmental or land use change. 5. :DWHU YDSRU DQG &22 ÀX[HV LQ WHUUHVWULDO HFRV\VWHPV RI 0H[LFR 0H[LFDQ HFRV\VWHPV SURYLGH ULFK RSSRUWXQLWLHV WR validate previous observations across ecosystems. 6RPHH[DPSOHVRIUHODWLRQVKLSVWKDWFRXOGEHWHVWHG and validated are those observed between phenology and CO2ÀX[HV 5LFKDUGVRQHWDO, 2010), control of *33 RQ 56 9DUJDV HW DO, 2011b), or the role of GURXJKW DQG ZDWHU SXOVHV 7KRPH\ HW DO, 2011). :KDWIROORZVDUHH[DPSOHVIURPPHDVXUHPHQWVDW 0H[)OX[VLWHVWRLOOXVWUDWHWKHGLYHUVLW\RISDWWHUQV and magnitudes of CO2ÀX[HV )RUH[DPSOHWKH2MXHORVVLWHORFDWHGLQDVHPLDULGJUDVVODQG 7DEOH,,, LVLGHDOIRULQYHVWLJDWLQJ the effect of precipitation pulses on NEE during the summer that result in higher CO2 emissions. Data from this site show that before precipitation events, QRFWXUQDO 1(( YDOXHV 5HFR E\ GH¿QLWLRQ  ZHUH  2 μmol CO2 m2 s–1 while after precipitation, pulses increased to values > 5 μmol CO2 m2 s–1 )LJ 7KH implications of these observations rely on climate change scenarios characterized by changes in frequency and intensity of precipitation and pulses.

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These changes in precipitation patterns can substantially affect carbon sequestration in semiarid rangelands by reducing or increasing water stress ZLWKLQWKHHFRV\VWHP 7KRPH\HWDO, 2011, Vargas HWDO, 2012b). $QRWKHUH[DPSOHFRPHVIURPVWXG\LQJWKH1RUWK American Monsoon, which is a regional phenomenon that provides most of the annual rainfall over large DUHDVRIQRUWKHUQ0H[LFR 9LYRQLHWDO, 2010). Data from the Tesopaco site, a tropical deciduous forest 7DEOH,,, VKRZVWKHLQÀXHQFHRIWKHPRQVRRQRYHU the seasonal trend of the normalized difference vegHWDWLRQLQGH[ 1'9,GHULYHGIURP02',6REVHUYDWLRQV 1((DQG(7 )LJ DVDPDUNHGYDULDELOLW\ LQWKHGLUHFWLRQDQGPDJQLWXGHRIÀX[HVDFURVVWKH growing season. It is estimated that this forest can sequester up to 374 g CO2 m-2 during the monsoon VHDVRQ 3pUH]5XL]HWDO, 2010). In urban sites, CO2ÀX[PHDVXUHPHQWVKDYHEHHQ used to evaluate emission inventories and develop PLWLJDWLRQ VWUDWHJLHV ZKLOH HQHUJ\ ÀX[HV FDQ EH useful for urbanization planning through a better

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measuring instruments and measurement methods; DQG  GHYHORSTXDOLW\DVVXUDQFHDQGFRQWURO 4$ 4& SURFHGXUHVRIUDZGDWDDQGSRVWSURFHVVLQJRI FRPSXWHG ÀX[HV LH JDS¿OOLQJ VHULHV SDUWLWLRQ 1((LQWR*33DQG56 7KLV4$4&PXVWFRPSO\ ZLWKLQWHUQDWLRQDOVWDQGDUGV 3DSDOHHWDO, 2006) to generate useful and consistent datasets for regional and global synthesis studies. 7RIDFLOLWDWHV\QWKHVLVVWXGLHVDQGPD[LPL]HGDWD use, the data storage and standardized post-processLQJFRXOGEHSURYLGHGE\H[LVWLQJF\EHULQIUDVWUXFWXUHLQGLIIHUHQWLQVWLWXWLRQVRI0H[)OX[PHPEHUV HJ, University of Alberta, Canada with its EnYLUR1HW SODWIRUP  ,QLWLDOO\ D VSHFL¿F 0H[)OX[ database will contain the products of site-level meaVXUHPHQWV LH, raw data) along with the processed data obtained following standardized protocols 3DSDOHHWDO 0H[)OX[KDVDGRSWHGDSROLF\ of submitting information from each study site to this database within a period of one year from its incorporation to the network. Only principal investigators will submit raw and processed data, and these will be freely available to the network memEHUVXQGHUDIDLUXVHSROLF\)LQDOO\0H[)OX[ZLOO promote training of human resources in the area of micrometeorological and biophysical measurements RIHQHUJ\DQG*+*ÀX[HV

7KHVKRUWWHUPFKDOOHQJHVIDFLQJ0H[)OX[DUH   developing protocols and standardization among sites IRUUHGXFLQJXQFHUWDLQWLHVLQWKHÀX[PHDVXUHPHQWV  HVWDEOLVKLQJUXOHVIRUDUFKLYLQJDQGSURFHVVLQJ GDWDZLWKLQWKH0H[)OX[GDWDEDVH  HVWDEOLVKLQJ clear and fair use data policies for all members acFRUGLQJWRWKHIXQGLQJVRXUFHIRUHDFKSURMHFW LH, GRPHVWLFDJHQFLHVDQGLQWHUQDWLRQDOIXQGLQJ DQG   the study sites must invest in measuring a common set of biological and physical parameters to describe the HFRV\VWHP HJ, vegetation structure, phenology, soil properties, management history) to better interpret REVHUYHGÀX[HV /DZHWDO, 2008). ,QWKHORQJWHUP0H[)OX[QHHGVDFRQWLQXRXVLQteraction with institutions and networks at the national and international levels. Important collaborations have been identified with the scientific networks VSRQVRUHGE\WKH&RQVHMR1DFLRQDOGH&LHQFLD\7HFQRORJtD &RQDF\W VXFKDVWKH5HG7HPiWLFDGHO$JXD 5(7$&ZDWHUUHVHDUFKQHWZRUN 5HG7HPiWLFDGH (FRVLVWHPDV (FR5HGHFRV\VWHPVUHVHDUFKQHWZRUN  and Red Temática de Medio Ambiente y SustentabilLGDG 5(0$6HQYLURQPHQWDOVXVWDLQDELOLW\UHVHDUFK network). Additionally, there is a strong link with the 3URJUDPD 0H[LFDQR GHO &DUERQR 30& 0H[LFDQ FDUERQSURJUDP WKH5HG0H[LFDQDGH,QYHVWLJDFLyQ (FROyJLFDD/DUJR3OD]R 0H[/7(50H[LFDQORQJ

334

R. Vargas et al.

term ecological research network), and international networks such as the North American Carbon Program &DUER1$ DQG7URSL'U\0H[)OX[LVH[SHFWHGWR KDYHDIXQGDPHQWDOUROHZLWKLQ)/8;1(7VLQFH0H[ican ecosystems are underrepresented and this limits the production of synthesis studies across regions, ZKLFKDUHLPSRUWDQWIRUVFLHQWL¿FXQGHUVWDQGLQJDQG SROLF\PDNLQJDFURVV1RUWK$PHULFD +DUPRQHWDO, 2011; Masek HWDO, 2011; Vargas HWDO, 2012a). We also suggest that long-term measurements ZLWKLQ 0H[)OX[ VKRXOG LQFRUSRUDWH RWKHU *+*V pollutants, aerosols and stable isotopes as technology EHFRPHVPRUHDFFHVVLEOHDQGPRUHVFLHQWLVWVMRLQWKH network. This new information could be integrated into models of ecosystem processes to update and validate previous observations and parameters. 0H[)OX[¶VORQJWHUPFKDOOHQJHLVWRVHHNWKHLQWHJUDWLRQRIUHVHDUFKHUVLQ¿HOGVRIFOLPDWHPRGHOLQJ mathematics, biogeochemistry, and social science related to policy making. Finally, we believe that it is essential to develop multi-institutional training DQG¿QDQFLQJPHFKDQLVPVIRUWKHPDLQWHQDQFHDQG operation of the study sites and secure the continuity RI0H[)OX[7KLVZLOORQO\EHDFKLHYHGLIWKHUHLV political will and evidence of the usefulness of value added products from the network for policy-making DQGVFLHQWL¿FDGYDQFHPHQW $FNQRZOHGJHPHQWV The authors acknowledge funding from Conacyt (FR5HG&RQDF\W IRUPHHWLQJVWKDWKDYHIDFLOLWDWed discussions between researchers and students. 59 LV JUDWHIXO IRU IXQGLQJ IURP &RQDF\W &LHQFLD Básica-152671). TA and CW thanks SEP-Conacyt. ASA and EGC thank the Inter-American Institute for Global Change Research, Tropi-Dry, supported by the National Science Foundation. EGC also acknowledgHVIXQGLQJIURPD&RQDF\W8&0H[XVVFKRODUVKLS CW gratefully acknowledges funding from Conacyt Ciencia Básica. EV acknowledges support from INE, MCE2, SMA-GDF and Singapore National Research Foundation trough SMART. GA and JLA acknowledge support from USAID and USFS. 5HIHUHQFHV Aubinet M., A. Grelle, A. Ibrom, U. Rannik, J. Moncrieff, T. Foken, A. S. Kowalski, P. H. Martin, P. Berbigier, C. Bernhofer, R. Clement, J. Elbers, A. Granier, T. Grunwald, K. Morgenstern, K. Pilegaard, C. Reb-

PDQQ:6QLMGHUV59DOHQWLQLDQG79HVDOD (VWLPDWHVRIWKHDQQXDOQHWFDUERQDQGZDWHUH[FKDQJH RIIRUHVWV7KH(XUR)OX[PHWKRGRORJ\$GY(FRO5HV 30, 113-175. Baldocchi D., E. Falge, L. H. Gu, R. Olson, D. Hollinger, S. Running, P. Anthoni, C. Bernhofer, K. Davis, R. Evans, J. Fuentes, A. Goldstein, G. Katul, B. Law, X. H. Lee, Y. Malhi, T. Meyers, W. Munger, W. Oechel, K. T. Paw, K. Pilegaard, H. P. Schmid, R. Valentini, S. Verma, T. Vesala, K. Wilson, and S. Wofsy, 2001. FLUXNET: A new tool to study the temporal and VSDWLDOYDULDELOLW\RIHFRV\VWHPVFDOHFDUERQGLR[LGH ZDWHUYDSRUDQGHQHUJ\ÀX[GHQVLWLHV%$P0HWHR URO6RF 82, 2415-2434. Baldocchi D. D., 2003. Assessing the eddy covariance WHFKQLTXHIRUHYDOXDWLQJFDUERQGLR[LGHH[FKDQJHUDWHV of ecosystems: Past, present and future. *ORE&KDQJH %LRO 9, 479-492. Baldocchi D., 2008. Breathing of the terrestrial biosphere: OHVVRQVOHDUQHGIURPDJOREDOQHWZRUNRIFDUERQGLR[LGH ÀX[PHDVXUHPHQWV\VWHPV$XVW-%RW 56, 1-26. Beer C., M. Reichstein, E. Tomelleri, P. Ciais, M. Jung, N. Carvalhais, C. Rodenbeck, M. A. Arain, D. Baldocchi, G. B. Bonan, A. Bondeau, A. Cescatti, G. Lasslop, A. Lindroth, M. Lomas, S. Luyssaert, H. Margolis, K. W. Oleson, O. Roupsard, E. Veenendaal, N. Viovy, C. Williams, F. I. Woodward and D. Papale, 2010. TerresWULDOJURVVFDUERQGLR[LGHXSWDNH*OREDOGLVWULEXWLRQ and covariation with climate. 6FLHQFH 329, 834-838. Bonan G. B., 2008. Forests and climate change: Forcings, IHHGEDFNVDQGWKHFOLPDWHEHQH¿WVRIIRUHVWV6FLHQFH 320, 1444-1449. Bond-Lamberty B. and A. Thomson, 2010. Temperature-associated increases in the global soil respiration record. 1DWXUH 464, 579-582. Burba G. G. and S. B. Verma, 2005. Seasonal and interannual variability in evapotranspiration of native tallgrass prairie and cultivated wheat ecosystems. $JU)RUHVW 0HWHRURO 135, 190-201. Canadell J. G., H. A. Mooney, D. D. Baldocchi, J. A. Berry, J. R. Ehleringer, C. B. Field, S. T. Gower, D. Y. Hollinger, J. E. Hunt, R. B. Jackson, S. W. Running, G. R. Shaver, W. Steffen, S. E. Trumbore, R. Valentini and B. Y. Bond, 2000. Carbon metabolism of the terrestrial biosphere: A multi-technique approach for improved understanding. (FRV\VWHPV 3, 115-130. &KDOOHQJHU$DQG-6REHUyQ/RVHFRVLVWHPDVWHUrestres. In &DSLWDOQDWXUDOGH0é[LFR &RQDELR(G  &RPLVLyQ1DFLRQDOSDUDHO&RQRFLPLHQWR\8VRGHOD %LRGLYHUVLGDG0p[LFRSS 87-108. Chapin F. S., P. A. Matson and H. A. Mooney, 2002. 3ULQFLSOHVRIWHUUHVWULDOHFRV\VWHPHFRORJ\. Springer, New York, 392 pp.

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