872 results on '"NEMITZ, EIKO"'
Search Results
2. A pre-whitening with block-bootstrap cross-correlation procedure for temporal alignment of data sampled by eddy covariance systems
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Vitale, Domenico, Fratini, Gerardo, Helfter, Carole, Hortnagl, Lukas, Kohonen, Kukka-Maaria, Mammarella, Ivan, Nemitz, Eiko, Nicolini, Giacomo, Rebmann, Corinna, Sabbatini, Simone, and Papale, Dario
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- 2024
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3. Emission inventory of inorganic trace gases from solid residential fuels over the National Capital Territory of India
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Arya, Rahul, Ahlawat, Sakshi, Yadav, Lokesh, Rani, Martina, Mondal, Arnab, Jangirh, Ritu, Kotnala, Garima, Choudhary, Nikki, Rai, Akansha, Saharan, Ummed Singh, Yadav, Pooja, Banoo, Rubiya, Sharma, Sudhir Kumar, Gurjar, Bhola Ram, Nemitz, Eiko, Hamilton, Jacqueline F., and Mandal, Tuhin Kumar
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- 2024
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4. Measurements of particulate methanesulfonic acid above the remote Arctic Ocean using a high resolution aerosol mass spectrometer
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Zhang, Yangmei, Sun, Junying, Shen, Xiaojing, Lal Chandani, Vipul, Du, Mao, Song, Congbo, Dai, Yuqing, Hu, Guoyuan, Yang, Mingxi, Tilstone, Gavin H., Jordan, Tom, Dall’Olmo, Giorgio, Liu, Quan, Nemitz, Eiko, Callaghan, Anna, Brean, James, Sommariva, Roberto, Beddows, David, Langford, Ben, Bloss, William, Acton, William, Harrison, Roy, Dall’Osto, Manuel, and Shi, Zongbo
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- 2024
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5. Analysing solid residential fuel usage patterns in rural and urban slums of Delhi: Implications for pollution reduction and sustainable practices
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Mondal, Arnab, Jangirh, Ritu, Arya, Rahul, Yadav, Lokesh, Ahlawat, Sakshi, Yadav, Pooja, Paliyal, Paramjeet Singh, Bobde, Prakash, Ghosh, Paulami, Mondal, Surajit, Rai, Akansha, Banoo, Rubiya, Chaudhary, Nikki, Rani, Martina, Kotnala, Garima, Nemitz, Eiko, Sharma, Sudhir Kumar, and Mandal, Tuhin Kumar
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- 2024
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6. Gap-filling eddy covariance methane fluxes: Comparison of machine learning model predictions and uncertainties at FLUXNET-CH4 wetlands
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Irvin, Jeremy, Zhou, Sharon, McNicol, Gavin, Lu, Fred, Liu, Vincent, Fluet-Chouinard, Etienne, Ouyang, Zutao, Knox, Sara Helen, Lucas-Moffat, Antje, Trotta, Carlo, Papale, Dario, Vitale, Domenico, Mammarella, Ivan, Alekseychik, Pavel, Aurela, Mika, Avati, Anand, Baldocchi, Dennis, Bansal, Sheel, Bohrer, Gil, Campbell, David I, Chen, Jiquan, Chu, Housen, Dalmagro, Higo J, Delwiche, Kyle B, Desai, Ankur R, Euskirchen, Eugenie, Feron, Sarah, Goeckede, Mathias, Heimann, Martin, Helbig, Manuel, Helfter, Carole, Hemes, Kyle S, Hirano, Takashi, Iwata, Hiroki, Jurasinski, Gerald, Kalhori, Aram, Kondrich, Andrew, Lai, Derrick YF, Lohila, Annalea, Malhotra, Avni, Merbold, Lutz, Mitra, Bhaskar, Ng, Andrew, Nilsson, Mats B, Noormets, Asko, Peichl, Matthias, Rey-Sanchez, A Camilo, Richardson, Andrew D, Runkle, Benjamin RK, Schäfer, Karina VR, Sonnentag, Oliver, Stuart-Haëntjens, Ellen, Sturtevant, Cove, Ueyama, Masahito, Valach, Alex C, Vargas, Rodrigo, Vourlitis, George L, Ward, Eric J, Wong, Guan Xhuan, Zona, Donatella, Alberto, Ma Carmelita R, Billesbach, David P, Celis, Gerardo, Dolman, Han, Friborg, Thomas, Fuchs, Kathrin, Gogo, Sébastien, Gondwe, Mangaliso J, Goodrich, Jordan P, Gottschalk, Pia, Hörtnagl, Lukas, Jacotot, Adrien, Koebsch, Franziska, Kasak, Kuno, Maier, Regine, Morin, Timothy H, Nemitz, Eiko, Oechel, Walter C, Oikawa, Patricia Y, Ono, Keisuke, Sachs, Torsten, Sakabe, Ayaka, Schuur, Edward A, Shortt, Robert, Sullivan, Ryan C, Szutu, Daphne J, Tuittila, Eeva-Stiina, Varlagin, Andrej, Verfaillie, Joeseph G, Wille, Christian, Windham-Myers, Lisamarie, Poulter, Benjamin, and Jackson, Robert B
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Earth Sciences ,Agricultural ,Veterinary and Food Sciences ,Biological Sciences ,Bioengineering ,Networking and Information Technology R&D (NITRD) ,Machine Learning and Artificial Intelligence ,Machine learning ,time series ,imputation ,gap-filling ,methane ,flux ,wetlands ,Agricultural and Veterinary Sciences ,Meteorology & Atmospheric Sciences ,Agricultural ,veterinary and food sciences ,Biological sciences ,Earth sciences - Abstract
Time series of wetland methane fluxes measured by eddy covariance require gap-filling to estimate daily, seasonal, and annual emissions. Gap-filling methane fluxes is challenging because of high variability and complex responses to multiple drivers. To date, there is no widely established gap-filling standard for wetland methane fluxes, with regards both to the best model algorithms and predictors. This study synthesizes results of different gap-filling methods systematically applied at 17 wetland sites spanning boreal to tropical regions and including all major wetland classes and two rice paddies. Procedures are proposed for: 1) creating realistic artificial gap scenarios, 2) training and evaluating gap-filling models without overstating performance, and 3) predicting half-hourly methane fluxes and annual emissions with realistic uncertainty estimates. Performance is compared between a conventional method (marginal distribution sampling) and four machine learning algorithms. The conventional method achieved similar median performance as the machine learning models but was worse than the best machine learning models and relatively insensitive to predictor choices. Of the machine learning models, decision tree algorithms performed the best in cross-validation experiments, even with a baseline predictor set, and artificial neural networks showed comparable performance when using all predictors. Soil temperature was frequently the most important predictor whilst water table depth was important at sites with substantial water table fluctuations, highlighting the value of data on wetland soil conditions. Raw gap-filling uncertainties from the machine learning models were underestimated and we propose a method to calibrate uncertainties to observations. The python code for model development, evaluation, and uncertainty estimation is publicly available. This study outlines a modular and robust machine learning workflow and makes recommendations for, and evaluates an improved baseline of, methane gap-filling models that can be implemented in multi-site syntheses or standardized products from regional and global flux networks (e.g., FLUXNET).
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- 2021
7. Estimation of ammonia deposition to forest ecosystems in Scotland and Sri Lanka using wind-controlled NH3 enhancement experiments
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Deshpande, Ajinkya G., Jones, Matthew R., van Dijk, Netty, Mullinger, Neil J., Harvey, Duncan, Nicoll, Robert, Toteva, Galina, Weerakoon, Gothamie, Nissanka, Sarath, Weerakoon, Buddhika, Grenier, Maude, Iwanicka, Agata, Duarte, Fred, Stephens, Amy, Ellis, Christopher J., Vieno, Massimo, Drewer, Julia, Wolseley, Pat A., Nanayakkara, Shamodi, Prabhashwara, Tharindu, Bealey, William J., Nemitz, Eiko, and Sutton, Mark A.
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- 2024
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8. Spatial distribution, sources, and health risk assessment of elements in road dust (
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Jangirh, Ritu, Yadav, Pooja, Mondal, Arnab, Yadav, Lokesh, Datta, Arindam, Saxena, Priyanka, Nemitz, Eiko, Gurjar, Bhola Ram, and Mandal, Tuhin Kumar
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- 2024
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9. Monitoring of carbon-water fluxes at Eurasian meteorological stations using random forest and remote sensing
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Xie, Mingjuan, Ma, Xiaofei, Wang, Yuangang, Li, Chaofan, Shi, Haiyang, Yuan, Xiuliang, Hellwich, Olaf, Chen, Chunbo, Zhang, Wenqiang, Zhang, Chen, Ling, Qing, Gao, Ruixiang, Zhang, Yu, Ochege, Friday Uchenna, Frankl, Amaury, De Maeyer, Philippe, Buchmann, Nina, Feigenwinter, Iris, Olesen, Jørgen E., Juszczak, Radoslaw, Jacotot, Adrien, Korrensalo, Aino, Pitacco, Andrea, Varlagin, Andrej, Shekhar, Ankit, Lohila, Annalea, Carrara, Arnaud, Brut, Aurore, Kruijt, Bart, Loubet, Benjamin, Heinesch, Bernard, Chojnicki, Bogdan, Helfter, Carole, Vincke, Caroline, Shao, Changliang, Bernhofer, Christian, Brümmer, Christian, Wille, Christian, Tuittila, Eeva-Stiina, Nemitz, Eiko, Meggio, Franco, Dong, Gang, Lanigan, Gary, Niedrist, Georg, Wohlfahrt, Georg, Zhou, Guoyi, Goded, Ignacio, Gruenwald, Thomas, Olejnik, Janusz, Jansen, Joachim, Neirynck, Johan, Tuovinen, Juha-Pekka, Zhang, Junhui, Klumpp, Katja, Pilegaard, Kim, Šigut, Ladislav, Klemedtsson, Leif, Tezza, Luca, Hörtnagl, Lukas, Urbaniak, Marek, Roland, Marilyn, Schmidt, Marius, Sutton, Mark A., Hehn, Markus, Saunders, Matthew, Mauder, Matthias, Aurela, Mika, Korkiakoski, Mika, Du, Mingyuan, Vendrame, Nadia, Kowalska, Natalia, Leahy, Paul G., Alekseychik, Pavel, Shi, Peili, Weslien, Per, Chen, Shiping, Fares, Silvano, Friborg, Thomas, Tallec, Tiphaine, Kato, Tomomichi, Sachs, Torsten, Maximov, Trofim, di Cella, Umberto Morra, Moderow, Uta, Li, Yingnian, He, Yongtao, Kosugi, Yoshiko, and Luo, Geping
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- 2023
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10. The potential of high temporal resolution automatic measurements of PM2.5 composition as an alternative to the filter-based manual method used in routine monitoring
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Twigg, Marsailidh M., Di Marco, Chiara F., McGhee, Elizabeth A., Braban, Christine F., Nemitz, Eiko, Brown, Richard J.C., Blakley, Kevin C., Leeson, Sarah R., Sanocka, Agnieszka, Green, David C., Priestman, Max, Riffault, Veronique, Bourin, Aude, Minguillón, Maria Cruz, Via, Marta, Ovadnevaite, Jurgita, Ceburnis, Darius, O'Dowd, Colin, Poulain, Laurent, Stieger, Bastian, Makkonen, Ulla, Rumsey, Ian C., Beachley, Gregory, Walker, John T., and Butterfield, David M.
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- 2023
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11. Response of organic aerosol to Delhi's pollution control measures over the period 2011–2018
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Cash, James M., Di Marco, Chiara, Langford, Ben, Heal, Mathew R., Mandal, Tuhin K., Sharma, Sudhir K., Gurjar, Bhola Ram, and Nemitz, Eiko
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- 2023
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12. Mapping the effects of ozone pollution and mixing on floral odour plumes and their impact on plant-pollinator interactions
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Langford, Ben, Ryalls, James M.W., Mullinger, Neil J., Hayden, Paul, Nemitz, Eiko, Pfrang, Christian, Robins, Alan, Touhami, Dalila, Bromfield, Lisa M., and Girling, Robbie D.
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- 2023
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13. FLUXNET-CH4: a global, multi-ecosystem dataset and analysis of methane seasonality from freshwater wetlands
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Delwiche, Kyle B, Knox, Sara Helen, Malhotra, Avni, Fluet-Chouinard, Etienne, McNicol, Gavin, Feron, Sarah, Ouyang, Zutao, Papale, Dario, Trotta, Carlo, Canfora, Eleonora, Cheah, You-Wei, Christianson, Danielle, Alberto, Ma Carmelita R, Alekseychik, Pavel, Aurela, Mika, Baldocchi, Dennis, Bansal, Sheel, Billesbach, David P, Bohrer, Gil, Bracho, Rosvel, Buchmann, Nina, Campbell, David I, Celis, Gerardo, Chen, Jiquan, Chen, Weinan, Chu, Housen, Dalmagro, Higo J, Dengel, Sigrid, Desai, Ankur R, Detto, Matteo, Dolman, Han, Eichelmann, Elke, Euskirchen, Eugenie, Famulari, Daniela, Fuchs, Kathrin, Goeckede, Mathias, Gogo, Sébastien, Gondwe, Mangaliso J, Goodrich, Jordan P, Gottschalk, Pia, Graham, Scott L, Heimann, Martin, Helbig, Manuel, Helfter, Carole, Hemes, Kyle S, Hirano, Takashi, Hollinger, David, Hörtnagl, Lukas, Iwata, Hiroki, Jacotot, Adrien, Jurasinski, Gerald, Kang, Minseok, Kasak, Kuno, King, John, Klatt, Janina, Koebsch, Franziska, Krauss, Ken W, Lai, Derrick YF, Lohila, Annalea, Mammarella, Ivan, Marchesini, Luca Belelli, Manca, Giovanni, Matthes, Jaclyn Hatala, Maximov, Trofim, Merbold, Lutz, Mitra, Bhaskar, Morin, Timothy H, Nemitz, Eiko, Nilsson, Mats B, Niu, Shuli, Oechel, Walter C, Oikawa, Patricia Y, Ono, Keisuke, Peichl, Matthias, Peltola, Olli, Reba, Michele L, Richardson, Andrew D, Riley, William, Runkle, Benjamin RK, Ryu, Youngryel, Sachs, Torsten, Sakabe, Ayaka, Sanchez, Camilo Rey, Schuur, Edward A, Schäfer, Karina VR, Sonnentag, Oliver, Sparks, Jed P, Stuart-Haëntjens, Ellen, Sturtevant, Cove, Sullivan, Ryan C, Szutu, Daphne J, Thom, Jonathan E, Torn, Margaret S, Tuittila, Eeva-Stiina, Turner, Jessica, Ueyama, Masahito, Valach, Alex C, Vargas, Rodrigo, Varlagin, Andrej, and Vazquez-Lule, Alma
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Earth Sciences ,Atmospheric Sciences ,Climate Action ,Geochemistry ,Physical Geography and Environmental Geoscience ,Atmospheric sciences ,Geoinformatics ,Physical geography and environmental geoscience - Abstract
Methane (CH4) emissions from natural landscapes constitute roughly half of global CH4 contributions to the atmosphere, yet large uncertainties remain in the absolute magnitude and the seasonality of emission quantities and drivers. Eddy covariance (EC) measurements of CH4 flux are ideal for constraining ecosystem-scale CH4 emissions due to quasi-continuous and high-temporal-resolution CH4 flux measurements, coincident carbon dioxide, water, and energy flux measurements, lack of ecosystem disturbance, and increased availability of datasets over the last decade. Here, we (1) describe the newly published dataset, FLUXNET-CH4 Version 1.0, the first open-source global dataset of CH4 EC measurements (available at https://fluxnet.org/data/fluxnet-ch4-community-product/, last access: 7 April 2021). FLUXNET-CH4 includes half-hourly and daily gap-filled and non-gap-filled aggregated CH4 fluxes and meteorological data from 79 sites globally: 42 freshwater wetlands, 6 brackish and saline wetlands, 7 formerly drained ecosystems, 7 rice paddy sites, 2 lakes, and 15 uplands. Then, we (2) evaluate FLUXNET-CH4 representativeness for freshwater wetland coverage globally because the majority of sites in FLUXNET-CH4 Version 1.0 are freshwater wetlands which are a substantial source of total atmospheric CH4 emissions; and (3) we provide the first global estimates of the seasonal variability and seasonality predictors of freshwater wetland CH4 fluxes. Our representativeness analysis suggests that the freshwater wetland sites in the dataset cover global wetland bioclimatic attributes (encompassing energy, moisture, and vegetation-related parameters) in arctic, boreal, and temperate regions but only sparsely cover humid tropical regions. Seasonality metrics of wetland CH4 emissions vary considerably across latitudinal bands. In freshwater wetlands (except those between 20g g€¯S to 20g g€¯N) the spring onset of elevated CH4 emissions starts 3g€¯d earlier, and the CH4 emission season lasts 4g€¯d longer, for each degree Celsius increase in mean annual air temperature. On average, the spring onset of increasing CH4 emissions lags behind soil warming by 1 month, with very few sites experiencing increased CH4 emissions prior to the onset of soil warming. In contrast, roughly half of these sites experience the spring onset of rising CH4 emissions prior to the spring increase in gross primary productivity (GPP). The timing of peak summer CH4 emissions does not correlate with the timing for either peak summer temperature or peak GPP. Our results provide seasonality parameters for CH4 modeling and highlight seasonality metrics that cannot be predicted by temperature or GPP (i.e., seasonality of CH4 peak). FLUXNET-CH4 is a powerful new resource for diagnosing and understanding the role of terrestrial ecosystems and climate drivers in the global CH4 cycle, and future additions of sites in tropical ecosystems and site years of data collection will provide added value to this database. All seasonality parameters are available at 10.5281/zenodo.4672601 (Delwiche et al., 2021). Additionally, raw FLUXNET-CH4 data used to extract seasonality parameters can be downloaded from https://fluxnet.org/data/fluxnet-ch4-community-product/ (last access: 7 April 2021), and a complete list of the 79 individual site data DOIs is provided in Table 2 of this paper.
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- 2021
14. Reduced-form and complex ACTM modelling for air quality policy development: A model inter-comparison
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Oxley, Tim, Vieno, Massimo, Woodward, Huw, ApSimon, Helen, Mehlig, Daniel, Beck, Rachel, Nemitz, Eiko, and Reis, Stefan
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- 2023
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15. Direct observations of CO2 emission reductions due to COVID-19 lockdown across European urban districts
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Nicolini, Giacomo, Antoniella, Gabriele, Carotenuto, Federico, Christen, Andreas, Ciais, Philippe, Feigenwinter, Christian, Gioli, Beniamino, Stagakis, Stavros, Velasco, Erik, Vogt, Roland, Ward, Helen C., Barlow, Janet, Chrysoulakis, Nektarios, Duce, Pierpaolo, Graus, Martin, Helfter, Carole, Heusinkveld, Bert, Järvi, Leena, Karl, Thomas, Marras, Serena, Masson, Valéry, Matthews, Bradley, Meier, Fred, Nemitz, Eiko, Sabbatini, Simone, Scherer, Dieter, Schume, Helmut, Sirca, Costantino, Steeneveld, Gert-Jan, Vagnoli, Carolina, Wang, Yilong, Zaldei, Alessandro, Zheng, Bo, and Papale, Dario
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- 2022
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16. Anthropogenic air pollutants reduce insect-mediated pollination services
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Ryalls, James M.W., Langford, Ben, Mullinger, Neil J., Bromfield, Lisa M., Nemitz, Eiko, Pfrang, Christian, and Girling, Robbie D.
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- 2022
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17. Towards long-term standardised carbon and greenhouse gas observations for monitoring Europe’s terrestrial ecosystems: a review
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Franz, Daniela, Acosta, Manuel, Altimir, Núria, Arriga, Nicola, Arrouays, Dominique, Aubinet, Marc, Aurela, Mika, Ayres, Edward, López-Ballesteros, Ana, Barbaste, Mireille, Berveiller, Daniel, Biraud, Sébastien, Boukir, Hakima, Brown, Timothy, Brümmer, Christian, Buchmann, Nina, Burba, George, Carrara, Arnaud, Cescatti, Allessandro, Ceschia, Eric, Clement, Robert, Cremonese, Edoardo, Crill, Patrick, Darenova, Eva, Dengel, Sigrid, D’Odorico, Petra, Filippa, Gianluca, Fleck, Stefan, Fratini, Gerardo, Fuß, Roland, Gielen, Bert, Gogo, Sébastien, Grace, John, Graf, Alexander, Grelle, Achim, Gross, Patrick, Grünwald, Thomas, Haapanala, Sami, Hehn, Markus, Heinesch, Bernard, Heiskanen, Jouni, Herbst, Mathias, Herschlein, Christine, Hörtnagl, Lukas, Hufkens, Koen, Ibrom, Andreas, Jolivet, Claudy, Joly, Lilian, Jones, Michael, Kiese, Ralf, Klemedtsson, Leif, Kljun, Natascha, Klumpp, Katja, Kolari, Pasi, Kolle, Olaf, Kowalski, Andrew, Kutsch, Werner, Laurila, Tuomas, de Ligne, Anne, Linder, Sune, Lindroth, Anders, Lohila, Annalea, Longdoz, Bernhard, Mammarella, Ivan, Manise, Tanguy, Jiménez, Sara Maraňón, Matteucci, Giorgio, Mauder, Matthias, Meier, Philip, Merbold, Lutz, Mereu, Simone, Metzger, Stefan, Migliavacca, Mirco, Mölder, Meelis, Montagnani, Leonardo, Moureaux, Christine, Nelson, David, Nemitz, Eiko, Nicolini, Giacomo, Nilsson, Mats B, de Beeck, Maarten Op, Osborne, Bruce, Löfvenius, Mikaell Ottosson, Pavelka, Marian, Peichl, Matthias, Peltola, Olli, Pihlatie, Mari, Pitacco, Andrea, Pokorný, Radek, Pumpanen, Jukka, Ratié, Céline, Rebmann, Corinna, Roland, Marilyn, Sabbatini, Simone, Saby, Nicolas PA, Saunders, Matthew, Schmid, Hans Peter, Schrumpf, Marion, Sedlák, Pavel, and Ortiz, Penelope Serrano
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Agriculture ,Land and Farm Management ,Agricultural ,Veterinary and Food Sciences ,Climate Action ,ICOS ,GHG exchange ,carbon cycle ,standardised monitoring ,observational network ,Agronomy & Agriculture ,Agriculture ,land and farm management - Abstract
Research infrastructures play a key role in launching a new generation of integrated long-Term, geographically distributed observation programmes designed to monitor climate change, better understand its impacts on global ecosystems, and evaluate possible mitigation and adaptation strategies. The pan-European Integrated Carbon Observation System combines carbon and greenhouse gas (GHG; CO 2 , CH 4 , N 2 O, H 2 O) observations within the atmosphere, terrestrial ecosystems and oceans. High-precision measurements are obtained using standardised methodologies, are centrally processed and openly available in a traceable and verifiable fashion in combination with detailed metadata. The Integrated Carbon Observation System ecosystem station network aims to sample climate and land-cover variability across Europe. In addition to GHG flux measurements, a large set of complementary data (including management practices, vegetation and soil characteristics) is collected to support the interpretation, spatial upscaling and modelling of observed ecosystem carbon and GHG dynamics. The applied sampling design was developed and formulated in protocols by the scientific community, representing a trade-off between an ideal dataset and practical feasibility. The use of open-Access, high-quality and multi-level data products by different user communities is crucial for the Integrated Carbon Observation System in order to achieve its scientific potential and societal value.
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- 2018
18. Potential and limitation of air pollution mitigation by vegetation and uncertainties of deposition-based evaluations
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Nemitz, Eiko, Vieno, Massimo, Carnell, Edward, Fitch, Alice, Steadman, Claudia, Cryle, Philip, Holland, Mike, Morton, R. Daniel, Hall, Jane, Mills, Gina, Hayes, Felicity, Dickie, Ian, Carruthers, David, Fowler, David, Reis, Stefan, and Jones, Laurence
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- 2020
19. A chronology of global air quality
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Fowler, David, Brimblecombe, Peter, Burrows, John, Heal, Mathew R., Grennfelt, Peringe, Stevenson, David S., Jowett, Alan, Nemitz, Eiko, Coyle, Mhairi, Liu, Xuejun, Chang, Yunhua, Fuller, Gary W., Sutton, Mark A., Klimont, Zbigniew, Unsworth, Mike H., and Vieno, Massimo
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- 2020
20. Emission estimates and inventories of non-methane volatile organic compounds from anthropogenic burning sources in India
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Stewart, Gareth J., Nelson, Beth S., Acton, W. Joe F., Vaughan, Adam R., Hopkins, James R., Yunus, Siti S.M., Hewitt, C. Nicholas, Wild, Oliver, Nemitz, Eiko, Gadi, Ranu, Sahu, Lokesh K., Mandal, Tuhin K., Gurjar, Bhola R., Rickard, Andrew R., Lee, James D., and Hamilton, Jacqueline F.
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- 2021
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21. Vertical profiles of biogenic volatile organic compounds as observed online at a tower in Beijing
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Zhang, Huina, Zhang, Yanli, Huang, Zhonghui, Acton, W. Joe F., Wang, Zhaoyi, Nemitz, Eiko, Langford, Ben, Mullinger, Neil, Davison, Brian, Shi, Zongbo, Liu, Di, Song, Wei, Yang, Weiqiang, Zeng, Jianqiang, Wu, Zhenfeng, Fu, Pingqing, Zhang, Qiang, and Wang, Xinming
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- 2020
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22. Improving Below‐Cloud Scavenging Coefficients of Sulfate, Nitrate, and Ammonium in PM2.5 and Implications for Numerical Simulation and Air Pollution Control
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Yao, Liquan, primary, Kong, Shaofei, additional, Nemitz, Eiko, additional, Vieno, Massimo, additional, Cheng, Yi, additional, Zheng, Huang, additional, Wang, Yuanlin, additional, Chen, Nan, additional, Hu, Yao, additional, Liu, Dantong, additional, Zhao, Tianliang, additional, Bai, Yongqing, additional, and Qi, Shihua, additional
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- 2024
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23. Temporal characteristics and vertical distribution of atmospheric ammonia and ammonium in winter in Beijing
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Wang, Qingqing, Zhang, Qi, Ma, Zhiqiang, Ge, Baozhu, Xie, Conghui, Zhou, Wei, Zhao, Jian, Xu, Weiqi, Du, Wei, Fu, Pingqing, Lee, James, Nemitz, Eiko, Cowan, Nicholas, Mullinger, Neil, Cheng, Xueling, Zhou, Libo, Yue, Siyao, Wang, Zifa, and Sun, Yele
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- 2019
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24. An Eddy-Covariance System for the Measurement of Surface/Atmosphere Exchange Fluxes of Submicron Aerosol Chemical Species—First Application Above an Urban Area
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Nemitz, Eiko, Jimenez, Jose L, Huffman, J Alex, Ulbrich, Ingrid M, Canagaratna, Manjula R, Worsnop, Doug R, and Guenther, Alex B
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Chemical Sciences ,Earth Sciences ,Engineering ,Meteorology & Atmospheric Sciences - Abstract
Until now, micrometeorological measurements of surface/ atmosphere exchange fluxes of submicron aerosol chemical components such as nitrate, sulfate or organics could only be made with gradient techniques. This article describes a novel setup to measure speciated aerosol fluxes by the more direct eddy covariance technique. The system is based on the Aerodyne quadrupole-based Aerosol Mass Spectrometer (Q-AMS), providing a quantitative measurement of aerosol constituents of environmental concern at a time resolution sufficient for eddy-covariance. The Q-AMS control software was modified to maximize duty cycle and statistics and enable fast data acquisition, synchronized with that of an ultrasonic anemometer. The detection limit of the Q-AMS based system for flux measurements ranges from 0.2 for NO3- to 15 ng m-2 s-1 for hydrocarbon-like organic aerosol (HOA), with an estimated precision of around 6 ng m-2 s-1, depending on aerosol loading. At common ambient concentrations the system is capable of resolving deposition velocity values < 1 mm s-1, sufficient for measurements of dry deposition to vegetation. First tests of the system in the urban environment (6 to 20 June 2003) in Boulder, CO, USA, reveal clear diurnal, presumably traffic related, patterns in the emission of HOA and NO3-, with indication of fast production of moderately oxygenated organic aerosol below the measurement height, averaging about 15% of the HOA emission. The average emission factor for HOA was 0.5 g (kg fuel)-1, similar to those found in previous studies. For NO3- an emission factor of 0.09 g (kg fuel)-1 was estimated, implying oxidation of 0.5% of the traffic derived NOx below the measurement height of 45 m. By contrast, SO42- fluxes were on average downward, with deposition velocities that increase with friction velocity from 0.4 to 4 mm s-1. Copyright © American Association for Aerosol Research.
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- 2008
25. Cloud Activating Properties of Aerosol Observed during CELTIC
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Stroud, Craig A, Nenes, Athanasios, Jimenez, Jose L, DeCarlo, Peter F, Huffman, J Alex, Bruintjes, Roelof, Nemitz, Eiko, Delia, Alice E, Toohey, Darin W, Guenther, Alex B, and Nandi, Sreela
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Atmospheric Sciences ,Meteorology & Atmospheric Sciences - Abstract
Measurements of aerosol size distribution, chemical composition, and cloud condensation nuclei (CCN) concentration were performed during the Chemical Emission, Loss, Transformation, and Interactions with Canopies (CELTIC) field program at Duke Forest in North Carolina. A kinetic model of the cloud activation of ambient aerosol in the chamber of the CCN instrument was used to perform an aerosol-CCN closure study. This study advances prior investigations by employing a novel fitting algorithm that was used to integrate scanning mobility particle sizer (SMPS) measurements of aerosol number size distribution and aerosol mass spectrometer (AMS) measurements of the mass size distribution for sulfate, nitrate, ammonium, and organics into a single, coherent description of the ambient aerosol in the size range critical to aerosol activation (around 100-nm diameter). Three lognormal aerosol size modes, each with a unique internally mixed composition, were used as input into the kinetic model. For the two smaller size modes, which control CCN number concentration, organic aerosol mass fractions for the defined cases were between 58% and 77%. This study is also unique in that the water vapor accommodation coefficient was estimated based on comparing the initial timing for CCN activation in the instrument chamber with the activation predicted by the kinetic model. The kinetic model overestimated measured CCN concentrations, especially under polluted conditions. Prior studies have attributed a positive model bias to an incomplete understanding of the aerosol composition, especially the role of organics in the activation process. This study shows that including measured organic mass fractions with an assumed organic aerosol speciation profile (pinic acid, fulvic acid, and levoglucosan) and an assumed organic aerosol solubility of 0.02 kg kg-1 still resulted in a significant model positive bias for polluted case study periods. The slope and y intercept for the CCN predicted versus CCN observed regression was found to be 1.9 and -180 cm-3, respectively. The overprediction generally does not exceed uncertainty limits but is indicative that a bias exists in the measurements or application of model. From this study, uncertainties in the particle number and mass size distributions as the cause for the model bias can be ruled out. The authors are also confident that the model is including the effects of growth kinetics on predicted activated number. However, one cannot rule out uncertainties associated with poorly characterized CCN measurement biases, uncertainties in assumed organic solubility, and uncertainties in aerosol mixing state. Sensitivity simulations suggest that assuming either an insoluble organic fraction or external aerosol mixing were both sufficient to reconcile the model bias. © 2007 American Meteorological Society.
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- 2007
26. Improving Below‐Cloud Scavenging Coefficients of Sulfate, Nitrate, and Ammonium in PM2.5 and Implications for Numerical Simulation and Air Pollution Control.
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Yao, Liquan, Kong, Shaofei, Nemitz, Eiko, Vieno, Massimo, Cheng, Yi, Zheng, Huang, Wang, Yuanlin, Chen, Nan, Hu, Yao, Liu, Dantong, Zhao, Tianliang, Bai, Yongqing, and Qi, Shihua
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AIR pollution control ,PRECIPITATION scavenging ,AIR pollutants ,RAINFALL ,PARTICULATE matter ,ATMOSPHERIC aerosols ,COMPUTER simulation - Abstract
Below‐cloud scavenging (BS) is often underestimated in chemical transport models (CTMs) due to inaccurate parameterizations of BS coefficient for fine particle (Λ) caused by a shortage of high‐time resolution field observations. Rainfall ions and related air pollutants were measured hourly in Central China (CC) during 2019. BS contributed to 37%–68% of wet deposition for SO42– ${\text{SO}}_{4}^{2\mbox{--}}$, NO3– ${\text{NO}}_{3}^{\mbox{--}}$, and NH4+ ${\text{NH}}_{4}^{+}$ (SNA). By a bulk method coupled with brute‐force search, the Λ (10−2–10 hr−1) was parameterized for SNA in PM2.5, which was 1–3 orders of magnitudes higher than theoretical calculations in CTMs. These chemical‐specific Λ parameterizations were validated by EMEP model. Compared to baselines, updated simulations for annual SNA wet deposition increased by 3.3%–20.4% and for mean PM2.5 SNA concentrations reduced by 1.2%–40%, capturing measurements better. The contributions of scavenged gases to wet deposition below cloud were calculated as 9%–73%, exhibiting discrepancies (2%–17% for HNO3 and 19%–90% for SO2) with previous modeling results as different Λ schemes adopted in CTMs. The nonlinearity between Λ and precipitation intensity causes frequency exerting stronger impact on aerosol burden than intensity and duration. Periodic light rain with a precipitation amount of 1–10 mm per event can eliminate 60% of SNA in PM2.5 and is suggested as a routine procedure to improve local air quality. Analyzing a typical washout process after a haze event in CC, BS could reduce PM2.5 SNA concentrations by 44%–54% derived from improved parameterizations. Plain Language Summary: The below‐cloud scavenging (BS) is a key process for removing atmospheric aerosols. An underestimation of BS for fine particle (PM2.5) is common in chemical transport models (CTMs) and biases simulations. A comprehensive observation was conducted for 1 year to improve parameterizations of BS coefficient for PM2.5 compounds (Λ). These parameterizations were assessed with a CTM. The updates increased the modeled wet deposition fluxes and decreased aerosol concentrations. These results mimicked observations better than baselines. The diversity of BS parameterizations in CTMs enhanced uncertainties of numerical simulation evaluations. The nonlinearity pattern of Λ between precipitation intensity implies frequency imposing stronger impact on aerosol burden than intensity and duration. This principle determines periodic light rain more suitable for cleaning air pollutants routinely. Utilizing the observational parameterizations, the importance of washout on clearing haze was revealed. This work can improve numerical simulations and air pollution control policies. Key Points: The parameterizations of below‐cloud scavenging coefficients for fine particle compounds were improvedThe reliability of chemical‐specific parameterizations was verified by a chemical transport modelThe implications of improved parameterizations for numerical simulations and air pollution control were elucidated [ABSTRACT FROM AUTHOR]
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- 2024
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27. Role of canopy‐scale photochemistry in modifying biogenic‐atmosphere exchange of reactive terpene species: Results from the CELTIC field study
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Stroud, Craig, Makar, Paul, Karl, Thomas, Guenther, Alex, Geron, Chris, Turnipseed, Andrew, Nemitz, Eiko, Baker, Brad, Potosnak, Mark, and Fuentes, Jose D
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Meteorology & Atmospheric Sciences - Abstract
A one-dimensional canopy model was used to quantify the impact of photochemistry in modifying biosphere-atmosphere exchange of trace gases. Canopy escape efficiencies, defined as the fraction of emission that escapes into the well-mixed boundary layer, were calculated for reactive terpene species. The modeled processes of emission, photochemistry, diffusive transport, and deposition were highly constrained based on intensive observations collected in a Loblolly Pine plantation at Duke Forest, North Carolina, during the CELTIC field study. Canopy top fluxes for isoprene and α,β-pinene were not significantly altered by photochemistry as calculated escape efficiencies were greater than 0.90 for both species, β-caryophyllene emission and photochemistry were added to the canopy model as a surrogate for the reactive sesquiterpene class of species, β-caryopyllene escape efficiencies of 0.30 were calculated for midday summertime conditions. Urbanization scenarios were also performed to assess the impact of pollution on modifying biosphere-atmosphere exchange. Modest changes in escape efficiencies were calculated for a wide range of anthropogenic hydrocarbon and NOx mixing ratios suggesting a simple parameterization of escape efficiency in terms of grid cell NOx may be possible for incorporating the impact of canopy scale photochemistry within biogenic emission processing systems for regional air quality and climate models. The inferred magnitude of sesquiterpene ozonolysis reactions has important implications on both daytime and nighttime radical formation in the canopy. Copyright 2005 by the American Geophysical Union.
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- 2005
28. Extreme Concentrations of Nitric Oxide Control Daytime Oxidation and Quench Nocturnal Oxidation Chemistry in Delhi during Highly Polluted Episodes
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Nelson, Beth S., Bryant, Daniel J., Alam, Mohammed S., Sommariva, Roberto, Bloss, William J., Newland, Mike J., Drysdale, Will S., Vaughan, Adam R., Acton, W. Joe F., Hewitt, C. Nicholas, Crilley, Leigh R., Swift, Stefan J., Edwards, Pete M., Lewis, Alastair C., Langford, Ben, Nemitz, Eiko, Shivani, Gadi, Ranu, Gurjar, Bhola R., Heard, Dwayne E., Whalley, Lisa K., Şahin, Ülkü A., Beddows, David C. S., Hopkins, James R., Lee, James D., Rickard, Andrew R., Hamilton, Jacqueline F., Nelson, Beth S., Bryant, Daniel J., Alam, Mohammed S., Sommariva, Roberto, Bloss, William J., Newland, Mike J., Drysdale, Will S., Vaughan, Adam R., Acton, W. Joe F., Hewitt, C. Nicholas, Crilley, Leigh R., Swift, Stefan J., Edwards, Pete M., Lewis, Alastair C., Langford, Ben, Nemitz, Eiko, Shivani, Gadi, Ranu, Gurjar, Bhola R., Heard, Dwayne E., Whalley, Lisa K., Şahin, Ülkü A., Beddows, David C. S., Hopkins, James R., Lee, James D., Rickard, Andrew R., and Hamilton, Jacqueline F.
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Delhi, India, suffers from periods of very poor air quality, but little is known about the chemical production of secondary pollutants in this highly polluted environment. During the postmonsoon period in 2018, extremely high nighttime concentrations of NOx (NO and NO2) and volatile organic compounds (VOCs) were observed, with median NOx mixing ratios of ∼200 ppbV (maximum of ∼700 ppbV). A detailed chemical box model constrained to a comprehensive suite of speciated VOC and NOx measurements revealed very low nighttime concentrations of oxidants, NO3, O3, and OH, driven by high nighttime NO concentrations. This results in an atypical NO3 diel profile, not previously reported in other highly polluted urban environments, significantly perturbing nighttime radical oxidation chemistry. Low concentrations of oxidants and high nocturnal primary emissions coupled with a shallow boundary layer led to enhanced early morning photo-oxidation chemistry. This results in a temporal shift in peak O3 concentrations when compared to the premonsoon period (12:00 and 15:00 local time, respectively). This shift will likely have important implications on local air quality, and effective urban air quality management should consider the impacts of nighttime emission sources during the postmonsoon period.
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- 2023
29. Qualitative impact assessment of land management interventions on ecosystem services (‘QEIA’). Report-2: integrated assessment
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Emmett, Bridget, Cosby, Jack, Bentley, Laura, Birnie, Jonathan, Botham, Marc, Bowes, Mike, Braban, Christine, Broughton, Richard, Burden, Annette, Carvell, Claire, Costa Domingo, G., Drewer, Julia, Evans, Chris, Feeney, Christopher, Fletcher, D., Garbutt, Angus, Gaskell, P., Goodenough, A., Hassin, A.E.J., Hunt, Merryn, Hutchins, Michael, Jackson, D., Jones, Laurence, Keenleyside, Clunie, Law, Ryan, Lucas, Owen T., Magowan, Elizabeth, Maskell, Lindsay, Matthews, Robert, McGowan, Al, Nemitz, Eiko, Newell-Price, Paul, Norton, Lisa, Pywell, Richard, Qu, Yueming, Short, Chris, Siriwardena, Gavin, Staddon, P., Staley, Joanna, Thomson, Amanda, Taylor, J., Urquhart, J., Wagner, Markus, Williams, John, Williams, Prysor, Woodcock, Ben, Bell, Chris, Emmett, Bridget, Cosby, Jack, Bentley, Laura, Birnie, Jonathan, Botham, Marc, Bowes, Mike, Braban, Christine, Broughton, Richard, Burden, Annette, Carvell, Claire, Costa Domingo, G., Drewer, Julia, Evans, Chris, Feeney, Christopher, Fletcher, D., Garbutt, Angus, Gaskell, P., Goodenough, A., Hassin, A.E.J., Hunt, Merryn, Hutchins, Michael, Jackson, D., Jones, Laurence, Keenleyside, Clunie, Law, Ryan, Lucas, Owen T., Magowan, Elizabeth, Maskell, Lindsay, Matthews, Robert, McGowan, Al, Nemitz, Eiko, Newell-Price, Paul, Norton, Lisa, Pywell, Richard, Qu, Yueming, Short, Chris, Siriwardena, Gavin, Staddon, P., Staley, Joanna, Thomson, Amanda, Taylor, J., Urquhart, J., Wagner, Markus, Williams, John, Williams, Prysor, Woodcock, Ben, and Bell, Chris
- Abstract
This project assessed the impacts of 741 potential land management actions, suitable for agricultural land in England, on the Farming & Countryside Programme’s Environmental Objectives (and therefore Environment Act targets and climate commitments) through 53 relevant environmental and cultural service indicators. The project used a combination of expert opinion and rapid evidence reviews, which included 1000+ pages of evidence in 10 separate reports with reference to over 2400 published studies, and an Integrated Assessment comprising expert-derived qualitative impact scores. The project has ensured that ELM schemes are evidence-based, offer good value for money, and contribute to SoS priorities for farming.
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- 2023
30. The potential of high temporal resolution automatic measurements of PM2.5 composition as an alternative to the filter-based manual method used in routine monitoring
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0000-0002-5462-3348, 0000-0003-4275-0152, 0000-0002-1765-6298, 0000-0001-6106-0996, 0009-0001-3132-3473, 0000-0001-5572-0871, 0000-0002-5935-8467, 0000-0002-5464-0391, 0000-0001-7201-0118, 0000-0002-9128-7881, 0000-0003-2946-7002, 0000-0002-7760-3438, Twigg, Marsailidh M., Di Marco, Chiara F., McGhee, Elizabeth A., Braban, Christine F., Nemitz, Eiko, Brown, Richard J.C., Blakley, Kevin C., Leeson, Sarah R., Sanocka, Agnieszka, Green, David C., Priestman, Max, Riffault, Veronique, Bourin, Aude, Minguillón, María Cruz, Via, Marta, Ovadnevaite, Jurgita, Ceburnis, Darius, O'Dowd, Colin, Poulain, Laurent, Stieger, Bastian, Makkonen, Ulla, Rumsey, Ian C., Beachley, Gregory, Walker, John T., Butterfield, David M., 0000-0002-5462-3348, 0000-0003-4275-0152, 0000-0002-1765-6298, 0000-0001-6106-0996, 0009-0001-3132-3473, 0000-0001-5572-0871, 0000-0002-5935-8467, 0000-0002-5464-0391, 0000-0001-7201-0118, 0000-0002-9128-7881, 0000-0003-2946-7002, 0000-0002-7760-3438, Twigg, Marsailidh M., Di Marco, Chiara F., McGhee, Elizabeth A., Braban, Christine F., Nemitz, Eiko, Brown, Richard J.C., Blakley, Kevin C., Leeson, Sarah R., Sanocka, Agnieszka, Green, David C., Priestman, Max, Riffault, Veronique, Bourin, Aude, Minguillón, María Cruz, Via, Marta, Ovadnevaite, Jurgita, Ceburnis, Darius, O'Dowd, Colin, Poulain, Laurent, Stieger, Bastian, Makkonen, Ulla, Rumsey, Ian C., Beachley, Gregory, Walker, John T., and Butterfield, David M.
- Abstract
Under the EU Air Quality Directive (AQD) 2008/50/EC member states are required to undertake routine monitoring of PM2.5 composition at background stations. The AQD states for PM2.5 speciation this should include at least: nitrate (NO3−), sulfate (SO42−), chloride (Cl−), ammonium (NH4+), sodium (Na+), potassium (K+), magnesium (Mg2+), calcium (Ca2+), elemental carbon (EC) and organic carbon (OC). Until 2017, it was the responsibility of each country to determine the methodology used to report the composition for the inorganic components of PM2.5. In August 2017 a European standard method of measurement of PM2.5 inorganic chemical components (NO3−, SO42−, Cl−, NH4+, Na+, K+, Mg2+, Ca2+) as deposited on filters (EN16913:2017) was published. From August 2019 this then became the European standard method. This filter method is labour-intensive and provides limited time resolution and is prone to losses of volatile compounds. There is therefore increasing interest in the use of alternative automated methods. For example, the UK reports hourly PM2.5 chemical composition using the Monitor for AeRosols and Gases in Ambient air (MARGA, Metrohm, NL). This study is a pre-assessment review of available data to demonstrate if or to what extent equivalence is possible using either the MARGA or other available automatic methods, including the Aerosol Chemical Speciation Monitor (ACSM, Aerodyne Research Inc. US) and the Ambient Ion Monitor (AIM, URG, US). To demonstrate equivalence three objectives were to be met. The first two objectives focused on data capture and were met by all three instruments. The third objective was to have less than a 50% expanded uncertainty compared to the reference method for each species. Analysis of this objective was carried out using existing paired datasets available from different regions around the world. It was found that the MARGA (2006–2019 model) had the potential to demonstrate equivalence for all species in the standard, though it was only t
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- 2023
31. Pandemic restrictions in 2020 highlight the significance of non-road NOx sources in central London
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Cliff, Samuel J., Drysdale, Will, Lee, James D., Helfter, Carole, Nemitz, Eiko, Metzger, Stefan, Barlow, Janet F., Cliff, Samuel J., Drysdale, Will, Lee, James D., Helfter, Carole, Nemitz, Eiko, Metzger, Stefan, and Barlow, Janet F.
- Abstract
Fluxes of nitrogen oxides (NOx = NO + NO2) and carbon dioxide (CO2) were measured using eddy covariance at the British Telecommunications (BT) Tower in central London during the coronavirus pandemic. Comparing fluxes to those measured in 2017 prior to the pandemic restrictions and the introduction of the Ultra-Low Emissions Zone (ULEZ) highlighted a 73 % reduction in NOx emissions between the two periods but only a 20 % reduction in CO2 emissions and a 32 % reduction in traffic load. Use of a footprint model and the London Atmospheric Emissions Inventory (LAEI) identified transport and heat and power generation to be the two dominant sources of NOx and CO2 but with significantly different relative contributions for each species. Application of external constraints on NOx and CO2 emissions allowed the reductions in the different sources to be untangled, identifying that transport NOx emissions had reduced by >73 % since 2017. This was attributed in part to the success of air quality policy in central London but crucially due to the substantial reduction in congestion that resulted from pandemic-reduced mobility. Spatial mapping of the fluxes suggests that central London was dominated by point source heat and power generation emissions during the period of reduced mobility. This will have important implications on future air quality policy for NO2 which, until now, has been primarily focused on the emissions from diesel exhausts.
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- 2023
32. Chloride (HCl ∕ Cl−) dominates inorganic aerosol formation from ammonia in the Indo-Gangetic Plain during winter: modeling and comparison with observations
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Pawar, Pooja V., Ghude, Sachin D., Govardhan, Gaurav, Acharja, Prodip, Kulkarni, Rachana, Kumar, Rajesh, Sinha, Baerbel, Sinha, Vinayak, Jena, Chinmay, Gunwani, Preeti, Adhya, Tapan Kumar, Nemitz, Eiko, Sutton, Mark A., Pawar, Pooja V., Ghude, Sachin D., Govardhan, Gaurav, Acharja, Prodip, Kulkarni, Rachana, Kumar, Rajesh, Sinha, Baerbel, Sinha, Vinayak, Jena, Chinmay, Gunwani, Preeti, Adhya, Tapan Kumar, Nemitz, Eiko, and Sutton, Mark A.
- Abstract
The Winter Fog Experiment (WiFEX) was an intensive field campaign conducted at Indira Gandhi International Airport (IGIA) Delhi, India, in the Indo-Gangetic Plain (IGP) during the winter of 2017–2018. Here, we report the first comparison in South Asia of high-temporal-resolution simulation of ammonia (NH3) along with ammonium (NH) and total NHx (i.e., NH3+ NH) using the Weather Research and Forecasting model coupled with chemistry (WRF-Chem) and measurements made using the Monitor for AeRosols and Gases in Ambient Air (MARGA) at the WiFEX research site. In the present study, we incorporated the Model for Simulating Aerosol Interactions and Chemistry (MOSAIC) aerosol scheme into WRF-Chem. Despite simulated total NHx values and variability often agreeing well with the observations, the model frequently simulated higher NH3 and lower NH concentrations than the observations. Under the winter conditions of high relative humidity (RH) in Delhi, hydrogen chloride (HCl) was found to promote the increase in the particle fraction of NH (which accounted for 49.5 % of the resolved aerosol in equivalent units), with chloride (Cl−) (29.7 %) as the primary anion. By contrast, the absence of chloride (HCl Cl−) chemistry in the standard WRF-Chem model results in the prediction of sulfate (SO) as the dominant inorganic aerosol anion. To understand the mismatch associated with the fraction of NHx in the particulate phase (NH NHx), we added HCl Cl− to the model and evaluated the influence of its chemistry by conducting three sensitivity experiments using the model: no HCl, base case HCl (using a published waste burning inventory), and 3 × base HCl run. We found that 3 × base HCl increased the simulated average NH by 13.1 µg m−3 and NHx by 9.8 µg m−3 concentration while reducing the average NH3 by 3.2 µg m−3, which is more in accord with the measurements. Thus HCl Cl− chemistry in the model increases total NHx concentration, which was further demonstrated by reducing NH3 emissions b
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- 2023
33. Modelling the Concentration and Deposition of Heavy Metals in the UK
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Dore, Anthony, Hallsworth, Stephen, Werner, Małgorzata, Kryza, Maciej, Nemitz, Eiko, Malcolm, Heath, Reis, Stefan, Fowler, David, Steyn, Douw, editor, and Mathur, Rohit, editor
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- 2014
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34. Eddy covariance measurements of black carbon emissions in central London
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Cheng, Zixuan, primary, Allan, James, additional, Hu, Dawei, additional, Nemitz, Eiko, additional, Langford, Ben, additional, Helfter, Carole, additional, Drysdale, Will, additional, Lee, James, additional, Cash, James, additional, Cliff, Sam, additional, Liu, Dantong, additional, and Rutambhara, Joshi, additional
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- 2023
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35. Pandemic restrictions in 2020 highlight the significance of non-road NOx sources in central London
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Cliff, Samuel J., primary, Drysdale, Will, additional, Lee, James D., additional, Helfter, Carole, additional, Nemitz, Eiko, additional, Metzger, Stefan, additional, and Barlow, Janet F., additional
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- 2023
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36. Chloride (HCl ∕ Cl−) dominates inorganic aerosol formation from ammonia in the Indo-Gangetic Plain during winter: modeling and comparison with observations
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Pawar, Pooja V., primary, Ghude, Sachin D., additional, Govardhan, Gaurav, additional, Acharja, Prodip, additional, Kulkarni, Rachana, additional, Kumar, Rajesh, additional, Sinha, Baerbel, additional, Sinha, Vinayak, additional, Jena, Chinmay, additional, Gunwani, Preeti, additional, Adhya, Tapan Kumar, additional, Nemitz, Eiko, additional, and Sutton, Mark A., additional
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- 2023
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37. Indoor Air Quality
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Lewis, A. C., Allan, James D., Carruthers, David, Carslaw, D.C., Fuller, Gary W, Harrison, Roy M., Heal, Mathew R, Nemitz, Eiko, Reeves, C. E., Carslaw, Nicola, Dengel, Andy, Dimitroulopoulou, Sani, Gupta, Rajat, Fisher, Matthew C, Fowler, David, Marner, Ben B., Moller, Sarah, Maggs, Richard, Murrells, Tim, Martin, N., Quincey, Paul, and Willis, Paul
- Abstract
People spend a substantial fraction of their lives indoors (often 80-90%) and so these locations can represent a significant fraction of exposure to air pollution. Indoor air quality is a complex phenomenon but has been studied far less than air quality outdoors. In the absence of indoor sources of pollution, indoor air quality is determined by ingress of outdoor air, balanced with pollutant loss processes such as deposition to surfaces and through ventilation. In reality most enclosed spaces have a wide range of indoor emissions including from buildings materials, furnishings, the use of combustion appliances such as gas and solid fuel cookers, boilers and stoves, the consumption of solvent-containing products, and the use of consumer products (e.g. cleaning and personal care products). Individuals themselves are a source of emissions that include CO2, human bio-effluents and biological aerosols such as viruses. Some factors are outside an occupant’s control, such as building fabric or ventilation in public spaces or the workplace, however individual behaviour and activities are a significant determinant of indoor air pollutant concentrations. Consequently, a person’s actions can directly influence the concentrations they experience. This contrasts with outdoors where concentrations are to a large degree controlled through the aggregation of collective societal emissions. Since dispersion is much more limited indoors, compared to outdoors, even modest emissions indoors can result in high indoor concentrations.There is extensive qualitative information on how individual processes, materials and activities can lead to emissions indoors, including the detailed chemical speciation of the pollutants released. Many of the key outdoor pollutants are found to be important indoors, such as particulate matter (PM2.5), nitrogen oxides (NOx), and carbon monoxide (CO), although there is limited evidence of whether the toxicity of PM indoors differs from outdoors. There are aspects of pollution found indoors that are notably different to outdoors. Mould and damp can lead to elevated concentrations of biological aerosols when compared to those found typically outdoors. The indoor environment can accumulate much higher concentrations of volatile organic compounds (VOCs) than are found outdoors in the UK, due to their release from construction and furnishing materials and use of cleaning and personal care products.Whilst comprehensive inventories exist that list the myriad different chemicals that are emitted indoors, AQEG found only limited information that places those emissions on a quantitative footing, e.g., expressing emissions of a pollutant as mass per unit of activity, person, or consumption. In this report, the National Atmospheric Emissions Inventory (NAEI) has been a key source of information on indoor emissions in the UK. Although the NAEI is not designed specifically for the purposes of evaluating indoor air quality, sources of pollution arising from buildings are significant to outdoor air quality and their emissions at a national scale are captured and reported as part of transboundary emissions obligations. Particularly notable are emissions of VOCs, of which >14% occur indoors according to the NAEI (for contrast only 0.1% of NOx and 0.7% of PM2.5 emissions occur indoors). Major sources include aerosol propellants and decorating products such as paints and varnishes.A complex mix of ventilation and product emission regulations and guidelines have an impact on indoor air quality, but these are not always well-integrated with one another or used to their best effect. Standards for acceptable ventilation rates are included in Buildings Regulations in the UK; high VOC content products such as paints have been regulated through EU Directives, and numerous labelling schemes exist for construction products across Europe, but not in the UK. Less well defined are standards for acceptable concentrations of air pollutant indoors. Advisory health-based guideline values on selected indoor air pollutants issued by WHO and UKHSA (formerly PHE) do not have any statutory underpinning. In the workplace there are limits on occupational exposure to a range of airborne chemicals. These assume that the time spent in these settings is limited and those exposed are healthy adults, so they are set at high time-weighted concentrations. Occupational indoor air quality standards are likely not appropriate for a wider population that includes children, elderly and vulnerable individuals.A major area of uncertainty identified relates to current concentrations of indoor air pollution in UK homes and their trends over time. Most AQEG reports on outdoor air quality can draw on extensive observational data collected through national, local authority and research networks, on many different pollutants, and often over multi-decadal periods. No such datasets exists for indoor air quality in the UK. Instead, the only quantitative evidence on indoor air quality comes from individual research studies in specific indoor micro-environments (e.g., homes, schools, transport, rail stations, shops etc.) with fragmented and inconsistent pollutant speciation. Most research studies report information for only a small number of pollutants over a short period of sampling, providing only a snapshot of concentrations and with limited data on occupant activities.Since it is impossible to measure everywhere at once, outdoor air quality management assumes that given suitable criteria, representative assessments of concentrations can be made from a limited number of representative monitoring locations such as roadside, urban background and rural. It is however challenging to characterise a ‘representative’ indoor space that can be used as a reference point or a baseline against which other locations can be compared. A consequence is that it is impossible to generate a holistic and quantitative picture of current concentrations in UK buildings, or how this may have changed over time. It is also challenging to use measurements to evaluate those processes that determine indoor air quality, or to draw general or widely applicable conclusions on the effectiveness of interventions. Compared to outdoors, conducting detailed observations in homes is practically difficult and resource intensive, and each experiment runs the risk of being unrepresentative of other indoor locations. What emerges from research measurements of indoor air is the exceptional heterogeneity of chemicals found, and with a far greater range of concentrations than are encountered in typical ambient outdoor air in the UK.There are currently rather limited capabilities to model and predict indoor concentrations (or personal exposure). For outdoor air, there is comprehensive model infrastructure to estimate concentrations of pollution at any given point in space or time, through combining emissions data, chemical mechanisms and meteorological fields. Outdoor models are routinely tested against observations to evaluate their performance, and in some cases, observations are used to improve model forecasts. The indoor environment lacks this same degree of predictive capability, in large part because of the uncertainty in potential contributing emission sources. This compromises attempts to estimate exposure and health effects, or the use of models to evaluate potential interventions. There are detailed chemical mechanisms that describe indoor gas and particle-phase reactions, developed as extensions of schemes used for outdoor models. However, these models frequently lack building and occupant-specific emission rates into indoor spaces, or parameterisation of ventilation, temperature, relative humidity, lighting, and air exchange of individual buildings. The key role played by occupant behaviours in controlling factors such as ventilation and frequency of use of consumer products that emit, means that identical homes can often experience widely differing levels of indoor air quality.Determining whether indoor or outdoor air quality is the greater contributor to overall exposure is not straightforward. For any individual, it will depend uniquely on time spent in each environment, their home, its location, ventilation, choices of activity indoors and crucially which pollutant is being considered. The home is also not the only indoor environment that people experience. Elevated concentrations of pollution have been reported in studies of air quality in UK schools and hospitals, of particular significance given they are occupied by more vulnerable groups. Transport micro-environments are also a significant route of exposure, inside cars, buses and trains and transport hub buildings. Looking across the literature, peak indoor reported concentrations of PM2.5 can often be higher than those that are experienced outdoors. For NO2 the picture is mixed; outdoors at the roadside concentrations are often higher than are typically reported indoors, except when there is unextracted gas cooking. For biological aerosols, carbon monoxide and many VOCs, literature reported indoor concentrations in the UK are often significantly higher than outdoors.There are numerous interventions that would likely improve indoor air quality including eliminating emissions from highly polluting sources such as solid fuel burners, improving building quality, and the development of lower emission product standards with accompanying labelling. Reducing emissions from these sources would also benefit outdoor air quality as well.Anticipated improvements in outdoor air quality, as set out in the Clean Air Strategy, should also feed through into better indoor air quality, since air exchange will remain a key factor in determining indoor concentrations. However, it should be noted that in some urban and road-side locations ozone concentrations are likely to increase and that if brought in to buildings nearby could increase rates of indoor air chemistry. There are direct opportunities to further improve indoor quality through increased ventilation in buildings (including homes, commercial and public spaces), an issue which has increased significantly in public prominence during the COVID-19 pandemic. The enclosed nature of indoor spaces makes them amenable to air quality improvement through active air filtration systems for particulate matter, although these may incur tradeoffs that include capital / operational costs and long-term changes in exposure to bioaerosols that may have uncertain impacts on health. Caution is noted regarding other air cleaning technologies such as those using UV light, ozone, peroxyl radicals or ionizing reactions, which have the potential to be detrimental to indoor air quality through the creation of harmful secondary pollutants.
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- 2022
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38. Evaluation of isoprene light response curves for bryophyte-dominated ecosystems and implications for atmospheric composition
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Langford, Ben, primary, Cash, James M, additional, Vieno, Massimo, additional, Heal, Mathew R, additional, Drewer, Julia, additional, Jones, Matthew R, additional, Leeson, Sarah R, additional, Simmons, Ivan, additional, Braban, Christine F, additional, and Nemitz, Eiko, additional
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- 2022
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39. Intercomparison of in situ measurements of ambient NH3: instrument performance and application under field conditions
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Twigg, Marsailidh M., primary, Berkhout, Augustinus J. C., additional, Cowan, Nicholas, additional, Crunaire, Sabine, additional, Dammers, Enrico, additional, Ebert, Volker, additional, Gaudion, Vincent, additional, Haaima, Marty, additional, Häni, Christoph, additional, John, Lewis, additional, Jones, Matthew R., additional, Kamps, Bjorn, additional, Kentisbeer, John, additional, Kupper, Thomas, additional, Leeson, Sarah R., additional, Leuenberger, Daiana, additional, Lüttschwager, Nils O. B., additional, Makkonen, Ulla, additional, Martin, Nicholas A., additional, Missler, David, additional, Mounsor, Duncan, additional, Neftel, Albrecht, additional, Nelson, Chad, additional, Nemitz, Eiko, additional, Oudwater, Rutger, additional, Pascale, Celine, additional, Petit, Jean-Eudes, additional, Pogany, Andrea, additional, Redon, Nathalie, additional, Sintermann, Jörg, additional, Stephens, Amy, additional, Sutton, Mark A., additional, Tang, Yuk S., additional, Zijlmans, Rens, additional, Braban, Christine F., additional, and Niederhauser, Bernhard, additional
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- 2022
- Full Text
- View/download PDF
40. Pandemic Restrictions in 2020 highlight the significance of non-road NOx sources in central London
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Cliff, Samuel J., primary, Drysdale, Will, additional, Lee, James D., additional, Helfter, Carole, additional, Nemitz, Eiko, additional, Metzger, Stefan, additional, and Barlow, Janet F., additional
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- 2022
- Full Text
- View/download PDF
41. Volatile organic compound speciation above and within a Douglas fir forest
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Copeland, Nichola, Cape, J. Neil, Nemitz, Eiko, and Heal, Mathew R.
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- 2014
- Full Text
- View/download PDF
42. Quantifying missing annual emission sources of heavy metals in the United Kingdom with an atmospheric transport model
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Dore, Anthony J., Hallsworth, Stephen, McDonald, Alan G., Werner, Małgorzata, Kryza, Maciej, Abbot, John, Nemitz, Eiko, Dore, Christopher J., Malcolm, Heath, Vieno, Massimo, Reis, Stefan, and Fowler, David
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- 2014
- Full Text
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43. Application of the EMEP Unified Model to the UK with a Horizontal Resolution of 5 × 5 km2
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Vieno, Massimo, Dore, Anthony J., Wind, Peter, Marco, Chiara Di, Nemitz, Eiko, Phillips, Gavin, Tarrasón, Leonor, Sutton, Mark A., Sutton, Mark A., editor, Reis, Stefan, editor, and Baker, Samantha M.H., editor
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- 2009
- Full Text
- View/download PDF
44. Biogenic and anthropogenic sources of isoprene and monoterpenes and their secondary organic aerosol in Delhi, India
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Bryant, Daniel J., Nelson, Beth S., Swift, Stefan J., Budisulistiorini, Sri Hapsari, Drysdale, Will S., Vaughan, Adam R., Newland, Mike J., Hopkins, James R., Cash, James M., Langford, Ben, Nemitz, Eiko, Acton, W. Joe F., Hewitt, C. Nicholas, Mandal, Tuhin, Gurjar, Bhola R., Shivani, Gadi, Ranu, Lee, James D., Rickard, Andrew R., and Hamilton, Jacqueline F.
- Subjects
Atmospheric Science ,Atmospheric Sciences - Abstract
Isoprene and monoterpene emissions to the atmosphere are generally dominated by biogenic sources. The oxidation of these compounds can lead to the production of secondary organic aerosol; however the impact of this chemistry in polluted urban settings has been poorly studied. Isoprene and monoterpenes can form secondary organic aerosol (SOA) heterogeneously via anthropogenic–biogenic interactions, resulting in the formation of organosulfate (OS) and nitrooxy-organosulfate (NOS) species. Delhi, India, is one of the most polluted cities in the world, but little is known about the emissions of biogenic volatile organic compounds (VOCs) or the sources of SOA. As part of the DELHI-FLUX project, gas-phase mixing ratios of isoprene and speciated monoterpenes were measured during pre- and post-monsoon measurement campaigns in central Delhi. Nocturnal mixing ratios of the VOCs were substantially higher during the post-monsoon (isoprene: (0.65±0.43) ppbv; limonene: (0.59±0.11) ppbv; α-pinene: (0.13±0.12) ppbv) than the pre-monsoon (isoprene: (0.13±0.18) ppbv; limonene: 0.011±0.025 (ppbv); α-pinene: 0.033±0.009) period. At night, isoprene and monoterpene concentrations correlated strongly with CO during the post-monsoon period. Filter samples of particulate matter less than 2.5 µm in diameter (PM2.5) were collected and the OS and NOS content analysed using ultra-high-performance liquid chromatography tandem mass spectrometry (UHPLC-MS2). Inorganic sulfate was shown to facilitate the formation of isoprene OS species across both campaigns. Sulfate contained within OS and NOS species was shown to contribute significantly to the sulfate signal measured via AMS. Strong nocturnal enhancements of NOS species were observed across both campaigns. The total concentration of OS and NOS species contributed an average of (2.0±0.9) % and (1.8±1.4) % to the total oxidized organic aerosol and up to a maximum of 4.2 % and 6.6 % across the pre- and post-monsoon periods, respectively. Overall, this study provides the first molecular-level measurements of SOA derived from isoprene and monoterpene in Delhi and demonstrates that both biogenic and anthropogenic sources of these compounds can be important in urban areas.
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- 2022
45. Eddy covariance measurements highlight sources of nitrogen oxide emissions missing from inventories for central London
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Drysdale, Will S., primary, Vaughan, Adam R., additional, Squires, Freya A., additional, Cliff, Sam J., additional, Metzger, Stefan, additional, Durden, David, additional, Pingintha-Durden, Natchaya, additional, Helfter, Carole, additional, Nemitz, Eiko, additional, Grimmond, C. Sue B., additional, Barlow, Janet, additional, Beevers, Sean, additional, Stewart, Gregor, additional, Dajnak, David, additional, Purvis, Ruth M., additional, and Lee, James D., additional
- Published
- 2022
- Full Text
- View/download PDF
46. Particle Size Distribution from Municipal Solid Waste Burning over National Capital Territory, India
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Arya, Rahul, primary, Ahlawat, Sakshi, additional, Yadav, Lokesh, additional, Jangirh, Ritu, additional, Mondal, Arnab, additional, Sharma, Sudhir Kumar, additional, Gurjar, Bhola Ram, additional, Nemitz, Eiko, additional, and Mandal, Tuhin Kumar, additional
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- 2022
- Full Text
- View/download PDF
47. Towards a climate-dependent paradigm of ammonia emission and deposition
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Sutton, Mark A., Reis, Stefan, Riddick, Stuart N., Dragosits, Ulrike, Nemitz, Eiko, Theobald, Mark R., Tang, Y. Sim, Braban, Christine F., Vieno, Massimo, Dore, Anthony J., Mitchell, Robert F., Wanless, Sarah, Daunt, Francis, Fowler, David, Blackall, Trevor D., Milford, Celia, Flechard, Chris R., Loubet, Benjamin, Massad, Raia, Cellier, Pierre, Personne, Erwan, Coheur, Pierre F., Clarisse, Lieven, Van Damme, Martin, Ngadi, Yasmine, Clerbaux, Cathy, Skjøth, Carsten Ambelas, Geels, Camilla, Hertel, Ole, Kruit, Roy J. Wichink, Pinder, Robert W., Bash, Jesse O., Walker, John T., Simpson, David, Horváth, László, Misselbrook, Tom H., Bleeker, Albert, Dentener, Frank, and de Vries, Wim
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- 2013
- Full Text
- View/download PDF
48. Passive breath monitoring of livestock: using factor analysis to deconvolve the cattle shed
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Langford, Ben, Cash, James, Beel, Georgia, Di Marco, Chiara F., Duthie, Carol-Anne, Haskell, Marie, Miller, Gemma, Nicoll, Laura, Roberts, Craig S., Nemitz, Eiko, Langford, Ben, Cash, James, Beel, Georgia, Di Marco, Chiara F., Duthie, Carol-Anne, Haskell, Marie, Miller, Gemma, Nicoll, Laura, Roberts, Craig S., and Nemitz, Eiko
- Abstract
Respiratory and metabolic diseases in livestock cost the agriculture sector billions each year, with delayed diagnosis a key exacerbating factor. Previous studies have shown the potential for breath analysis to successfully identify incidence of disease in a range of livestock. However, these techniques typically involve animal handling, the use of nasal swabs or fixing a mask to individual animals to obtain a sample of breath. Using a cohort of 26 cattle as an example, we show how the breath of individual animals within a herd can be monitored using a passive sampling system, where no such handling is required. These benefits come at the cost of the desired breath samples unavoidably mixed with the complex cocktail of odours that are present within the cattle shed. Data were analysed using positive matrix factorisation (PMF) to identify and remove non-breath related sources of VOC. In total three breath factors were identified (endogenous-, non-endogenous breath and rumen) and seven factors related to other sources within and around the cattle shed (e.g. foodcattle feed, traffic, urine and faeces). Simulation of a respiratory disease within the herd showed that the abnormal change in breath composition were captured in the residuals of the 10 factor PMF solution, highlighting the importance of their inclusion as part of the breath fraction. Increasing the number of PMF factors to 17 saw the identification of a "diseased" factor, which coincided with the visits of the three "diseased" cattle to the breath monitor platform. This work highlights the important role that factor analysis techniques can play in analysing passive breath monitoring data.
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- 2022
49. Seasonality of isoprene emissions and oxidation products above the remote Amazon
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Langford, Ben, House, Emily Roseanne, Valach, Alex C., Hewitt, C.N., Artaxo, Paulo, Barkley, Michael P., de Brito, Joel F., Carnell, Ed, Davison, Brian, MacKenzie, Angus Robert, Marais, Eloise A., Newland, Mike J., Rickard, Andrew R., Shaw, Marvin David, Yáñez-Serrano, Ana Maria, Nemitz, Eiko, Langford, Ben, House, Emily Roseanne, Valach, Alex C., Hewitt, C.N., Artaxo, Paulo, Barkley, Michael P., de Brito, Joel F., Carnell, Ed, Davison, Brian, MacKenzie, Angus Robert, Marais, Eloise A., Newland, Mike J., Rickard, Andrew R., Shaw, Marvin David, Yáñez-Serrano, Ana Maria, and Nemitz, Eiko
- Abstract
The Amazon rainforest is the largest source of isoprene emissions to the atmosphere globally. Under low nitric oxide (NO) conditions (i.e. at NO mixing ratios less than about 40 pptv), isoprene reacts rapidly with hydroxyl (OH) to form isoprene-derived peroxy radicals (ISOPOO), which subsequently react with the hydroperoxyl radical (HO2) to form isoprene epoxydiols (IEPOX). IEPOX compounds are efficient precursors to the formation of secondary organic aerosols (SOA). Natural isoprene emissions, therefore, have the potential to influence cloudiness, rainfall, radiation balance and climate. Here, we present the first seasonal analysis of isoprene emissions and concentrations above the Amazon based on eddy covariance flux measurements made at a remote forest location. We reveal the forest to maintain a constant emission potential of isoprene throughout the year (6.9 mg m-2 h-1). The emission potential of isoprene is calculated by normalising the measured fluxes to a set of standard conditions (303 K and 1500 µmol m-2 s-1). During the wet season a factor of two reduction in absolute emissions was observed but this is explained entirely on the basis of meteorology and leaf area index, not by a change in isoprene emissions potential. Using an innovative analysis of the isoprene fluxes, in combination with measurements of its oxidation products and detailed chemical box-modelling, we explore whether concentrations of IEPOX follow the same seasonal cycle as the isoprene precursor. Our analysis implies that during the dry season (Sep-Jan) air pollution from regional biomass burning provides a modest increase in NO concentrations (indirectly inferred from a combination of other anthropogenic tracer measurements and box-modelling) which creates a competing oxidation pathway for ISOPOO; rather than forming IEPOX, alternative products are formed with less propensity to produce aerosol. This competition decreases IEPOX formation rates by a factor of two in the dry season compared
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- 2022
50. Ozone mitigates the adverse effects of diesel exhaust pollutants on ground-active invertebrates in wheat
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Ryalls, James M.W., Staton, Tom, Mullinger, Neil, Bromfield, Lisa M., Langford, Ben, Pfrang, Christian, Nemitz, Eiko, Blande, James D., Girling, Robbie D., Ryalls, James M.W., Staton, Tom, Mullinger, Neil, Bromfield, Lisa M., Langford, Ben, Pfrang, Christian, Nemitz, Eiko, Blande, James D., and Girling, Robbie D.
- Abstract
There is growing evidence to demonstrate that air pollution is affecting invertebrates both directly (e.g., causing physiological stress responses) and indirectly (e.g., via changes in host plant chemistry and/or by disruption of communication by volatile odours). Many of the studies to-date have focused upon winged insects and disruption of in-flight foraging. Therefore, in this study we investigated how the community composition of predominantly ground-dwelling invertebrates in fields of winter wheat are affected by two of the most ubiquitous lower tropospheric air pollutants, diesel exhaust emissions (including nitrogen oxides–NOx) and ozone (O3), both individually and in combination, over 2 years. Pitfall traps, located within the rings of a Free-Air Diesel and Ozone Enrichment (FADOE) facility, were used to sample invertebrates. The facility consisted of eight 8 m-diameter rings, which allowed elevation of the pollutants above ambient levels (ca 49–60 ppb NOx and 35–39 ppb O3) but within levels currently defined as safe for the environment by the Environmental Protection Agency. The invertebrates collected were taxonomically identified and characterised by diet specialisation, mobility and functional group. Taxonomic richness and Shannon’s diversity index were calculated. Even under the relatively low levels of air pollution produced, there were adverse impacts on invertebrate community composition, with greater declines in the abundance and taxonomic richness of invertebrates in the diesel exhaust treatment compared with O3 treatment. In the combined treatment, pollutant levels were lower, most likely because NOx and O3 react with one another, and consequently a lesser negative effect was observed on invertebrate abundance and taxonomic richness. Specialist-feeding and winged invertebrate species appeared to be more sensitive to the impacts of the pollutants, responding more negatively to air pollution treatments than generalist feeders and wingless species, r
- Published
- 2022
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