On Transient Climate Change at the Cretaceous−Paleogene Boundary
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Effect of Heterogeneous Oxidative Aging on Light Absorption by Biomass Burning Organic Aerosol
Aerosol Science and Technology ISSN: 0278-6826 (Print) 1521-7388 (Online) Journal homepage: https://www.tandfonline.com/loi/uast20 Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol Eleanor C. Browne, Xiaolu Zhang, Jonathan P. Franklin, Kelsey J. Ridley, Thomas W. Kirchstetter, Kevin R. Wilson, Christopher D. Cappa & Jesse H. Kroll To cite this article: Eleanor C. Browne, Xiaolu Zhang, Jonathan P. Franklin, Kelsey J. Ridley, Thomas W. Kirchstetter, Kevin R. Wilson, Christopher D. Cappa & Jesse H. Kroll (2019) Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol, Aerosol Science and Technology, 53:6, 663-674, DOI: 10.1080/02786826.2019.1599321 To link to this article: https://doi.org/10.1080/02786826.2019.1599321 View supplementary material Accepted author version posted online: 26 Mar 2019. Published online: 15 Apr 2019. Submit your article to this journal Article views: 321 View Crossmark data Full Terms & Conditions of access and use can be found at https://www.tandfonline.com/action/journalInformation?journalCode=uast20 AEROSOL SCIENCE AND TECHNOLOGY 2019, VOL. 53, NO. 6, 663–674 https://doi.org/10.1080/02786826.2019.1599321 Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol Eleanor C. Brownea , Xiaolu Zhangb , Jonathan P. Franklinc, Kelsey J. Ridleyc, Thomas W. Kirchstetterd,e, Kevin R. Wilsonf , Christopher D. Cappag , and Jesse H. Krollc aDepartment of Chemistry and Cooperative Institute for Research -
Are Black Carbon and Soot the Same? Title Page
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Atmos. Chem. Phys. Discuss., 12, 24821–24846, 2012 Atmospheric www.atmos-chem-phys-discuss.net/12/24821/2012/ Chemistry ACPD doi:10.5194/acpd-12-24821-2012 and Physics © Author(s) 2012. CC Attribution 3.0 License. Discussions 12, 24821–24846, 2012 This discussion paper is/has been under review for the journal Atmospheric Chemistry Are black carbon and Physics (ACP). Please refer to the corresponding final paper in ACP if available. and soot the same? P. R. Buseck et al. Are black carbon and soot the same? Title Page P. R. Buseck1,2, K. Adachi1,2,3, A. Gelencser´ 4, E.´ Tompa4, and M. Posfai´ 4 Abstract Introduction 1School of Earth and Space Exploration, Arizona State University, Tempe, AZ 85282, USA Conclusions References 2 Department of Chemistry and Biochemistry, Arizona State University, Tempe, AZ 85282, USA Tables Figures 3Atmospheric Environment and Applied Meteorology Research Department, Meteorological Research Institute, Tsukuba, Ibaraki, Japan 4Department of Earth and Environmental Sciences, University of Pannonia, Veszprem,´ J I Hungary J I Received: 1 September 2012 – Accepted: 3 September 2012 – Published: 21 September 2012 Back Close Correspondence to: P. R. Buseck ([email protected]) Full Screen / Esc Published by Copernicus Publications on behalf of the European Geosciences Union. Printer-friendly Version Interactive Discussion 24821 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract ACPD The climate change and environmental literature, including that on aerosols, is replete with mention of black carbon (BC), but neither reliable samples nor standards exist. 12, 24821–24846, 2012 Thus, there is uncertainty about its exact nature. -
Elsevier First Proof
CLGY 00558 a0005 Trophic Structure E Preisser, University of Massachusetts at Amherst, Amherst, MA, USA ª 2007 Elsevier B.V. All rights reserved. Introduction Further Reading Control of Trophic Structure Energy transfer from producers to higher Factors Affecting Control of Trophic Structure trophic levels s0005 Introduction emphasizes the role(s) played by nutrient limitation and energetic inputs to producers and the subsequent effi- p0005 Trophic structure is defined as the partitioning of biomass ciency of energy transfer between trophic levels in between trophic levels (subsets of an ecological commu- determining the biomass accumulation at each trophic nity that gather energy and nutrients in similar ways, that level. The second category, top-down control, empha- is, producers, carnivores). The forces controlling biomass sizes the importance of predation in producing patterns accumulation at each trophic level have been a central of biomass accumulation that are often at odds with those concern of ecology dating from the early twentieth-cen- predicted byPROOF energy inputs alone. While recognizing the tury work of Elton and Lindeman. While interspecific differences between these two factors, it is also important interactions such as omnivory and intraguild predation to emphasize that both bottom-up and top-down factors can make it difficult to assign many organisms to a single represent extremes along a continuum of importance for trophic level, several broadly defined trophic levels are regulatory control. While ecologists debate the extent nonetheless clearly distinguishable. Primary producers, to which bottom-up versus top-down control influence autotrophic organisms (primarily plants and algae) that trophic structure in particular ecosystems, there is a broad convert light or chemical energy into biomass, make up consensus that both need to be considered when consid- the basal trophic level. -
DEEP SEA LEBANON RESULTS of the 2016 EXPEDITION EXPLORING SUBMARINE CANYONS Towards Deep-Sea Conservation in Lebanon Project
DEEP SEA LEBANON RESULTS OF THE 2016 EXPEDITION EXPLORING SUBMARINE CANYONS Towards Deep-Sea Conservation in Lebanon Project March 2018 DEEP SEA LEBANON RESULTS OF THE 2016 EXPEDITION EXPLORING SUBMARINE CANYONS Towards Deep-Sea Conservation in Lebanon Project Citation: Aguilar, R., García, S., Perry, A.L., Alvarez, H., Blanco, J., Bitar, G. 2018. 2016 Deep-sea Lebanon Expedition: Exploring Submarine Canyons. Oceana, Madrid. 94 p. DOI: 10.31230/osf.io/34cb9 Based on an official request from Lebanon’s Ministry of Environment back in 2013, Oceana has planned and carried out an expedition to survey Lebanese deep-sea canyons and escarpments. Cover: Cerianthus membranaceus © OCEANA All photos are © OCEANA Index 06 Introduction 11 Methods 16 Results 44 Areas 12 Rov surveys 16 Habitat types 44 Tarablus/Batroun 14 Infaunal surveys 16 Coralligenous habitat 44 Jounieh 14 Oceanographic and rhodolith/maërl 45 St. George beds measurements 46 Beirut 19 Sandy bottoms 15 Data analyses 46 Sayniq 15 Collaborations 20 Sandy-muddy bottoms 20 Rocky bottoms 22 Canyon heads 22 Bathyal muds 24 Species 27 Fishes 29 Crustaceans 30 Echinoderms 31 Cnidarians 36 Sponges 38 Molluscs 40 Bryozoans 40 Brachiopods 42 Tunicates 42 Annelids 42 Foraminifera 42 Algae | Deep sea Lebanon OCEANA 47 Human 50 Discussion and 68 Annex 1 85 Annex 2 impacts conclusions 68 Table A1. List of 85 Methodology for 47 Marine litter 51 Main expedition species identified assesing relative 49 Fisheries findings 84 Table A2. List conservation interest of 49 Other observations 52 Key community of threatened types and their species identified survey areas ecological importanc 84 Figure A1. -
As an Approach to the Cretaceous–Palaeogene Mass Extinction Event F
Geobiology (2009), 7, 533–543 DOI: 10.1111/j.1472-4669.2009.00213.x The environmental disaster of Aznalco´llar (southern Spain) as an approach to the Cretaceous–Palaeogene mass extinction event F. J. RODRI´ GUEZ-TOVAR1 ANDF.J.MARTI´ N-PEINADO2 1Departamento de Estratigrafı´a y Paleontologı´a, Universidad de Granada, Granada, Spain 2Departamento de Edafologı´a, Universidad de Granada, Granada, Spain ABSTRACT Biotic recovery after the Cretaceous–Palaeogene (K–Pg) impact is one unsolved question concerning this mass extinction event. To evaluate the incidence of the K–Pg event on biota, and the subsequent recovery, a recent environmental disaster has been analysed. Areas affected by the contamination disaster of Azna´ lcollar (province of Sevilla, southern Spain) in April 1998 were studied and compared with the K–Pg event. Several similarities (the sudden impact, the high levels of toxic components, especially in the upper thin lamina and the incidence on biota) and differences (the time of recovery and the geographical extension) are recognized. An in-depth geochemical analysis of the soils reveals their acidity (between 1.83 and 2.11) and the high concentration ) of pollutant elements, locally higher than in the K–Pg boundary layer: values up to 7.0 mg kg 1 for Hg, ) ) ) ) 2030.7 mg kg 1 for As, 8629.0 mg kg 1 for Pb, 86.8 mg kg 1 for Tl, 1040.7 mg kg 1 for Sb and 93.3– 492.7 p.p.b. for Ir. However, less than 10 years after the phenomenon, a rapid initial recovery in biota colonizing the contaminated, ‘unfavourable’, substrate is registered. -
Regime Shifts Between Macrophytes and Phytoplankton – Concepts Beyond Shallow Lakes, Unravelling Stabilizing Mechanisms and Practical Consequences
Limnetica, 29 (2): x-xx (2011) Limnetica, 34 (2): 467-480 (2015). DOI: 10.23818/limn.34.35 c Asociación Ibérica de Limnología, Madrid. Spain. ISSN: 0213-8409 Regime shifts between macrophytes and phytoplankton – concepts beyond shallow lakes, unravelling stabilizing mechanisms and practical consequences Sabine Hilt∗ Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 301, 12587 Berlin, Germany. ∗ Corresponding author: [email protected] 2 Received: 04/11/2014 Accepted: 11/06/2015 ABSTRACT Regime shifts between macrophytes and phytoplankton – concepts beyond shallow lakes, unravelling stabilizing mechanisms and practical consequences Feedback mechanisms between macrophytes and water clarity resulting in the occurrence of alternative stable states have been described in a theoretical concept for shallow lakes. Here, I review recent studies applying the concept to other freshwater systems, unravelling stabilizing mechanisms and discussing consequences of regime shifts. Recent modelling studies predict that abrupt changes between clear and turbid water states can also occur in lowland rivers, both in time and in space. These findings were supported by long-term data from rivers in Spain and Germany. A deep lake model revealed that submerged macrophytes may also significantly reduce phytoplankton biomass by 50-15 % in 100-11 m deep and oligotrophic lakes. Some of the mechanisms stabilizing clear-water conditions are still far from fully understood. Available data suggest that the macrophyte community composition affects number and type of mechanisms stabilizing clear-water conditions. Allelopathic effects of macrophytes on phytoplankton are no longer doubted, however, bacterial colonization of macrophytes and phytoplankton, phytoplankton interactions, local adaptations and strain-specific sensitivities have been found to modulate these interactions. -
The Value of Kol River Salmon Refuge's Ecosystem Services
REPORT The Value of Kol River Salmon Refuge’s Ecosystem Services Research conducted by University of Vermont’s Department of Community Development & Applied Economics and Gund Institute for Ecological Economics Authored by: Charles Kerchner, Roelof Boumans, and William Boykin-Morris Date Report: November 23, 2008 Prepared for and funded by: Wild Salmon Center List of Tables and Figures………………………………………………………………………………...……………….iii Executive Summary….......………………………………………………………………………………..………………….iv Chapter 1: Introduction………………………………………………………………………………………………………1 1.1 Research Objective.……………………………………………………………………………………2 1.2 Background…………………………………………………………………..………..2 Chapter 2: Ecosystem Goods, Ecosystem Services, and Market Failure………………...…………4 2.1 Why Is This Important?…………………………………………….……………………………….5 2.2 Valuation Typology……………………………………………………………………...…………….6 Chapter 3: Methods 3.1 Step 1: Ecosystem Service Quantification in KOL RAV Model……...…...…10 3.1.1 Metadata: GIS Data Used for Land Use Land Cover...…………………....11 3.2 Ecosystem Service Valuatin in KOL RAV Model……………………………...……13 3.2.1 Benefits Transfer………………………………..………………………………………......…13 3.2.2 Benefits Transfer – Meta-analysis………………………………………...…………14 3.2.3 Site Specific Valuation for Water Surface ……………………………….…….18 3.3 Step 3 & 4: Kol Refuge Ecosystem Service Evaluation Model (KRESEM)………………………..………………...23 3.3.1 Step 3: GIS Compnonent of KRESEM…………………………………..……….24 3.3.2 Step 4: Development of SIMILE Interface and Land Cover Change Scenarios………………………………….……...25 Chapter 4: Results………………………………………………………………………………………………………...…..26 -
Variation in Environmental Conditions in a Subtidal Prey Refuge: Effects of Salinity Stress, Food Availability and Predation on Mussels in a Fjord System
Vol. 422: 201–210, 2011 MARINE ECOLOGY PROGRESS SERIES Published January 31 doi: 10.3354/meps08911 Mar Ecol Prog Ser Variation in environmental conditions in a subtidal prey refuge: effects of salinity stress, food availability and predation on mussels in a fjord system Stephen R. Wing1,*, James J. Leichter2 1Department of Marine Science, 310 Castle Street, University of Otago, Dunedin 9054, New Zealand 2Scripps Institution of Oceanography, University of California at San Diego, 9500 Gilman Drive, La Jolla, California 92093, USA ABSTRACT: Prey refuges are fundamental structural features in communities. We investigated vari- ability in environmental conditions within a subtidal prey refuge for the blue mussel Mytilus edulis galloprovincialis formed by the persistent low-salinity layer (LSL) in Doubtful Sound, New Zealand. Multi-year observations and fine-scale oceanographic surveys along the axis of Doubtful Sound show strong spatial gradients in salinity, temperature, chlorophyll a (chl a) and nitrate concentrations. Mean surface salinity ranged from ~5 in the inner fjord zone to 15 in the mid-fjord, and 25 to 30 in the entrance zone. A marked subsurface maximum in chl a was observed below the LSL at 3 to 7 m depth. Adult blue mussels were confined to the LSL with a sharp decline in abundance from the entrance to the inner regions of the fjord. In contrast, mussel recruitment was observed both within and below the LSL to 10 m depth, with highest recruitment in the mid-fjord zone at 6 m depth. To test whether patterns in growth and survival in the absence of predation were coincident with food sup- ply and salinity stress, we transplanted mussels in predator exclusion cages at depths of 2, 4, 6, and 8 m within inner, mid-, and entrance fjord zones and measured growth over 213 d. -
Zooplankton Diel Vertical Migration During Antarctic Summer
Deep–Sea Research I 162 (2020) 103324 Contents lists available at ScienceDirect Deep-Sea Research Part I journal homepage: http://www.elsevier.com/locate/dsri Zooplankton diel vertical migration during Antarctic summer John A. Conroy a,*, Deborah K. Steinberg a, Patricia S. Thibodeau a,1, Oscar Schofield b a Virginia Institute of Marine Science, William & Mary, Gloucester Point, VA, 23062, USA b Center for Ocean Observing Leadership, Department of Marine and Coastal Sciences, School of Environmental and Biological Sciences, Rutgers University, New Brunswick, NJ, 08901, USA ARTICLE INFO ABSTRACT Keywords: Zooplankton diel vertical migration (DVM) during summer in the polar oceans is presumed to be dampened due Southern Ocean to near continuous daylight. We analyzed zooplankton diel vertical distribution patterns in a wide range of taxa Mesopelagic zone along the Western Antarctic Peninsula (WAP) to assess if DVM occurs, and if so, what environmental controls Copepod modulate DVM in the austral summer. Zooplankton were collected during January and February in paired day- Krill night, depth-stratifiedtows through the mesopelagic zone along the WAP from 2009-2017, as well as in day and Salp Pteropod night epipelagic net tows from 1993-2017. The copepod Metridia gerlachei, salp Salpa thompsoni, pteropod Limacina helicina antarctica, and ostracods consistently conducted DVM between the mesopelagic and epipelagic zones. Migration distance for M. gerlachei and ostracods decreased as photoperiod increased from 17 to 22 h daylight. The copepods Calanoides acutus and Rhincalanus gigas, as well as euphausiids Thysanoessa macrura and Euphausia crystallorophias, conducted shallow (mostly within the epipelagic zone) DVMs into the upper 50 m at night. -
Diel Horizontal Migration of Zooplankton: Costs and Benefits Of
Freshwater Biology (2002) 47, 343–365 FRESHWATER BIOLOGY SPECIAL REVIEW Diel horizontal migration of zooplankton: costs and benefits of inhabiting the littoral R. L. BURKS,* D. M. LODGE,* E. JEPPESEN† and T. L. LAURIDSEN† *Department of Biological Sciences, University of Notre Dame, Notre Dame, IN, U.S.A. †Department of Lake and Estuarine Ecology, National Environmental Research Institute, Vejlsøvej, Silkeborg, Denmark SUMMARY 1. In some shallow lakes, Daphnia and other important pelagic consumers of phyto- plankton undergo diel horizontal migration (DHM) into macrophytes or other structures in the littoral zone. Some authors have suggested that DHM reduces predation by fishes on Daphnia and other cladocerans, resulting in a lower phytoplankton biomass in shallow lakes than would occur without DHM. The costs and benefits of DHM, and its potential implications in biomanipulation, are relatively unknown, however. 2. In this review, we compare studies on diel vertical migration (DVM) to assess factors potentially influencing DHM (e.g. predators, food, light, temperature, dissolved oxygen, pH). We first provide examples of DHM and examine avoidance by Daphnia of both planktivorous (PL) fishes and predacious invertebrates. 3. We argue that DHM should be favoured when the abundance of macrophytes is high (which reduces planktivory) and the abundance of piscivores in the littoral is sufficient to reduce planktivores. Food in the littoral zone may favour DHM by daphnids, but the quality of these resources relative to pelagic phytoplankton is largely unknown. 4. We suggest that abiotic conditions, such as light, temperature, dissolved oxygen and pH, are less likely to influence DHM than DVM because weaker gradients of these conditions occur horizontally in shallow lakes relative to vertical gradients in deep lakes. -
Shallow Water As a Refuge Habitat for Fish and Crustaceans in Non-Vegetated Estuaries: an Example from Chesapeake Bay
MARINE ECOLOGY PROGRESS SERIES Vol. 99: 1-16, 1993 Published September 2 Mar. Ecol. Prog. Ser. l Shallow water as a refuge habitat for fish and crustaceans in non-vegetated estuaries: an example from Chesapeake Bay Gregory M. Ruiz l, Anson H. Hines l, Martin H. posey2 'Smithsonian Environmental Research Center, PO Box 28, Edgewater, Maryland 21037, USA 'Department of Biological Sciences, University of North Carolina at Wilmington, Wilmington, North Carolina 28403. USA ABSTRACT. Abundances and size-frequency distributions of common epibenth~cflsh and crustaceans were compared among 3 depth zones (1-35, 35-70, 71-95 cm) of the Rhode River, a subestuary of Chesapeake Bay, USA. In the absence of submerged aquatic vegetation (SAV),inter- and intraspccific size segregation occurred by depth from May to October, 1989-1992. Small species (Palaemonetes pugjo, Crangon septernspjnosa, Fundulus heteroclitus, F majaljs, Rhithropanope~lsharrisii, Apeltes quadracus, Gobiosorna boscj) were most abundant at water depths <70 cm. Furthermore, the propor- tion of small individuals decreased significantly with depth for 7 of 8 species, with C. septemsp~nosa being the exception, exhibiting no size change with increasing depth. These distributional patterns were related to depth-dependent predalion risk. Large species (Callinectes sap~dus,Leiostomus xan- thurus, and Micropogonias undulatus), known predators of some of the small species, were often most abundant in deep water (>70 cm). In field experiments, mortality of tethered P pugio (30 to 35 mm), small E heteroclitus (40 to 50 mm), and small C. sapjdus (30 to 70 mm) increased significantly with depth. Wc hypothesize that predation risk was size-dependent, creating the observed intra- and inter- specific size differences among depth zones. -
Articles and Detrital Matter
Biogeosciences, 7, 2851–2899, 2010 www.biogeosciences.net/7/2851/2010/ Biogeosciences doi:10.5194/bg-7-2851-2010 © Author(s) 2010. CC Attribution 3.0 License. Deep, diverse and definitely different: unique attributes of the world’s largest ecosystem E. Ramirez-Llodra1, A. Brandt2, R. Danovaro3, B. De Mol4, E. Escobar5, C. R. German6, L. A. Levin7, P. Martinez Arbizu8, L. Menot9, P. Buhl-Mortensen10, B. E. Narayanaswamy11, C. R. Smith12, D. P. Tittensor13, P. A. Tyler14, A. Vanreusel15, and M. Vecchione16 1Institut de Ciencies` del Mar, CSIC. Passeig Mar´ıtim de la Barceloneta 37-49, 08003 Barcelona, Spain 2Biocentrum Grindel and Zoological Museum, Martin-Luther-King-Platz 3, 20146 Hamburg, Germany 3Department of Marine Sciences, Polytechnic University of Marche, Via Brecce Bianche, 60131 Ancona, Italy 4GRC Geociencies` Marines, Parc Cient´ıfic de Barcelona, Universitat de Barcelona, Adolf Florensa 8, 08028 Barcelona, Spain 5Universidad Nacional Autonoma´ de Mexico,´ Instituto de Ciencias del Mar y Limnolog´ıa, A.P. 70-305 Ciudad Universitaria, 04510 Mexico,` Mexico´ 6Woods Hole Oceanographic Institution, MS #24, Woods Hole, MA 02543, USA 7Integrative Oceanography Division, Scripps Institution of Oceanography, La Jolla, CA 92093-0218, USA 8Deutsches Zentrum fur¨ Marine Biodiversitatsforschung,¨ Sudstrand¨ 44, 26382 Wilhelmshaven, Germany 9Ifremer Brest, DEEP/LEP, BP 70, 29280 Plouzane, France 10Institute of Marine Research, P.O. Box 1870, Nordnes, 5817 Bergen, Norway 11Scottish Association for Marine Science, Scottish Marine Institute, Oban,