Trophic Transfer of Mercury in a Subtropical Coral Reef Food Web

Total Page:16

File Type:pdf, Size:1020Kb

Trophic Transfer of Mercury in a Subtropical Coral Reef Food Web Trophic Transfer of Mercury in a Subtropical Coral Reef Food Web _______________________________________________________________________ A Thesis Presented to The Faculty of the College of Arts and Sciences Florida Gulf Coast University In Partial Fulfillment Of the Requirement for the Degree of Master of Science ________________________________________________________________________ By Christopher Tyler Lienhardt 2015 APPROVAL SHEET This thesis is submitted in partial fulfillment of the requirements for the degree of Master of Science ____________________________ Christopher Tyler Lienhardt Approved: July 2015 ____________________________ Darren G. Rumbold, Ph.D. Committee Chair / Advisor ____________________________ Michael L. Parsons, Ph.D. ____________________________ Ai Ning Loh, Ph. D. The final copy of this thesis has been examined by the signatories, and we find that both the content and the form meet acceptable presentation standards of scholarly work in the above mentioned discipline. i Acknowledgments This research would not have been possible without the support and encouragement of numerous friends and family. First and foremost I would like to thank my major advisor, Dr. Darren Rumbold, for giving me the opportunity to play a part in some of the great research he is conducting, and add another piece to the puzzle that is mercury biomagnification research. The knowledge, wisdom and skills imparted unto me over the past three years, I cannot thank him enough for. I would also like to thank Dr. Michael Parsons for giving me a shot to be a part of the field team and assist in the conducting of our research. I also owe him thanks for his guidance and the nature of his graduate courses, which helped prepare me to take on such a task. I would also like to thank Dr. Ai Ning Loh, for her comments and feedback on this thesis, and as someone who pushed me to pursue graduate school after working in her geochemistry laboratory as an undergraduate. I would also like to thank my friends and fellow graduate students Rheannon Ketover and Lacey Rains, your backing to apply to the program and support throughout it has been irreplaceable. Thanks are also owed to Alex Leynse, Amanda Ellsworth, Ashley Brandt, Nicole Fronczkowski, Megan Conkling, Adam Catasus, and Jeff Zingre (all from FGCU) for their assistance in collecting and processing samples. Finally, I am especially grateful to my mother Jamie Lienhardt and my best friend Lillie Simmons, for their moral support and constant encouragement throughout the many ups and downs that are the graduate school experience. ii Abstract Mercury is a widespread and damaging toxic metal that is trophically transferred through food webs. Coral reefs present an interesting dynamic in that they are comprised of complex food webs containing a high number of lateral or horizontal links that do not always end in top predators, thus possibly reducing trophic transfer. Therefore, the objective of the study was to assess the efficiency of trophic transfer in a coral reef food web, using mercury as the tracer. Concentrations of mercury and stable isotopes of nitrogen (δ15N) and carbon (δ13C) were measured in fish from two sites near the coastal waters of Long Key, Florida. The relationship between mercury and δ15N can be used to estimate biomagnification across the food web (i.e., trophic magnification slope, food web magnification factor). Using mercury and stable isotopes of nitrogen and carbon as tracers assisted in quantifying the efficiency at which coral reef ecosystems transfer these and other bioaccumulative toxins (e.g., ciguatoxins, etc.) through the food web, while also increasing our understanding of the associated flow of energy in the system. A total of 242 samples were collected from April 2012 through December 2013 using spear guns, hook and line, and hand collection techniques. Individual Hg concentrations ranged from 17.33 µg/kg in a gray angelfish (Pomacanthus arcuatus) to 3,317 µg/kg in a great barracuda (Sphyraena barracuda) at Long Key Hard Bottom, and 19.01 µg/kg in a rock beauty angelfish (Holacanthus tricolor) to 6,842 µg/kg in a porkfish (Anisotremus virginicus) at Tennessee Reef. Variability in both fish size and δ15N increased the variance in tissue Hg concentration both intra- and inter-specifically. As observed in other systems, the log transformed Hg concentrations in the food web, pooled across species, were significantly iii related to δ15N. The trophic magnification slope (i.e., slope of Log [Hg] regressed on δ15N), as an estimate of the biomagnification rate of Hg in the subtropical coral reef food web was 0.23 ± 0.03 (±95% confidence interval) at Tennessee Reef and 0.16 ± 0.04 for Long Key Hard Bottom. When δ15N was translated to trophic level, the food web magnification factor (calculated from slope of Log [Hg] regressed on trophic level) were 7.8 and 3.4 for Tennessee Reef and Long Key Hard Bottom, respectively. Although there was some evidence to support significant differences between the two sites (which could have been due to differences in water quality), this difference in slopes could also be a result of unbalanced sampling design. Nonetheless, these results clearly demonstrate that Hg is biomagnified through subtropical coral reef ecosystems and that the transfer efficiency (i.e., slopes) were consistent with previous reports for marine ecosystems. iv Table of contents Acknowledgments ............................................................................................................i Abstract .......................................................................................................................... ii Table of contents ............................................................................................................ iv List of Tables................................................................................................................... v List of Figures ................................................................................................................ vi Introduction ..................................................................................................................... 1 Objectives .................................................................................................................... 9 Significance ................................................................................................................. 9 Methods ........................................................................................................................ 10 Study Area ................................................................................................................. 10 Sample Collection and Processing ............................................................................. 11 Mercury Analysis ...................................................................................................... 12 Stable Isotope Analysis .............................................................................................. 13 Data Analysis ............................................................................................................ 14 Results ........................................................................................................................... 15 Variability in Mercury Concentration as a Function of Fish Size ................................ 16 Variability in Mercury Concentration as a Function of Location ................................ 17 Variability in Mercury Concentration in Relation to Stable Isotopes of Carbon and Nitrogen .................................................................................................................... 19 Trophic Magnification Slope (TMS) and Food Web Magnification Factor (FWMF) .. 21 Discussion ..................................................................................................................... 23 Conclusions ............................................................................................................... 38 Literature Cited ............................................................................................................. 39 v List of Tables Table 1. Summary of mercury concentration, total length, stable isotopes of δ13C and δ15N, and trophic level of invertebrate and finfish taxa collected from Tennessee Reef Light (TRL)………………………………………………………………………………56 Table 2. Summary of mercury concentration, total length, stable isotopes of δ13C and δ15N, and trophic level of invertebrate and finfish taxa collected from Long Key Hard Bottom (LKH)…………………………………………………………………………....57 Table 3. Coefficient of determination (r2) values for regression models for various relationships involving fish species at Tennessee Reef…………………………………...58 Table 4. Coefficient of determination (r2) values for regression models for various relationships involving fish species at Long Key Hard Bottom………………………….58 Table 5. Values for trophic magnification slopes of Total Hg biomagnification through food webs of different ecosystems as reported in the published literature……………….59 Table 6. Water quality conditions based on quarterly sampling from May 2010 – September 2013 at the two nearby sites (adapted from the FIU SERC Florida Keys National Marine Sanctuary). ………………………………………………………………………………60 vi List of Figures Figure 1. Map of study area where samples were collected off Long Key, FL………….61 Figure 2. (a) Relationship between log Hg (µg/kg) and total length (cm) in individuals at Tennessee
Recommended publications
  • Biomagnification of Methylmercury in a Marine Plankton Ecosystem
    EGU2020-1695, updated on 01 Oct 2021 https://doi.org/10.5194/egusphere-egu2020-1695 EGU General Assembly 2020 © Author(s) 2021. This work is distributed under the Creative Commons Attribution 4.0 License. Biomagnification of methylmercury in a marine plankton ecosystem Peipei Wu1, Emily Zakem2,3, Stephanie Dutkiewicz2, and Yanxu Zhang1 1School of Atmospheric Sciences, Nanjing University, Nanjing, Jiangsu, China ([email protected]) 2Department of Earth, Atmospheric, and Planetary Sciences, Massachusetts Institute of Technology, USA 3Department of Biological Sciences, University of Southern California, Los Angeles,USA Methylmercury is greatly bioconcentrated and biomagnified in marine plankton ecosystems, and these communities form the basis of marine food webs. Therefore, evaluating the potential exposure of methylmercury to higher trophic levels, including humans, requires a better understanding of its distribution in the ocean and the factors that control its biomagnification. In this study, a coupled physical/ecological model was used to simulate the trophic transfer of monomethylmercury (MMHg) in a marine plankton ecosystem. The model includes phytoplankton, a microbial community, herbivorous zooplankton (HZ), and carnivorous zooplankton (CZ). The model captured both shorter food chains in oligotrophic regions, with small HZ feeding on small phytoplankton, and longer chains in higher nutrient conditions, with larger HZ feeding on larger phytoplankton and larger CZ feeding on larger HZ. In the model, trophic dilution occurred in the food webs that involved small zooplankton, as the grazing fluxes of small zooplankton were insufficient to accumulate more MMHg in themselves than in their prey. The model suggested that biomagnification was more prominent in large zooplankton and that the microbial community played an important role in the trophic transfer of MMHg.
    [Show full text]
  • Calculation of Critical Loads for Cadmium, Lead and Mercury
    Calculation of critical loads for cadmium, lead and mercury Commissioned by the Dutch Ministries of Agriculture, Nature and Food Quality and of Housing, Spatial Planning and Environment 2 Alterra-report 1104 Calculation of critical loads for cadmium, lead and mercury Background document to a Mapping Manual on Critical Loads of cadmium, lead and mercury W. de Vries G. Schütze S. Lofts E. Tipping M. Meili P. F.A.M. Römkens J.E. Groenenberg Alterra-report 1104 Alterra, Wageningen, 2005 ABSTRACT Vries, W. de, G. Schütze, S. Lofts, E. Tipping, M. Meili, P.F.A.M. Römkens and J.E. Groenenberg, 2005. Calculation of critical loads for cadmium, lead and mercury. Background document to a Mapping Manual on Critical Loads of cadmium, lead and mercury. Wageningen, Alterra, Alterra-report 1104. 143 blz.; 1 fig; 13 tables.; 53 refs This report on heavy metals provides up-to-date methodologies to derive critical loads for the heavy metals cadmium (Cd), lead (Pb) and mercury (Hg) for both terrestrial and aquatic ecosystems. It presents background information to a Manual on Critical Loads for those metals. Focus is given to the methodologies and critical limits that have to be used to derive critical loads can be derived for Cd, Pb and Hg in view of : (i) ecotoxicological effects for either terrestrial or aquatic ecosystems.and (ii) human health effects for either terrestrial or aquatic ecosystems. For Hg, a separate approach is described to estimate critical levels in precipitation in view of human health effects due to the consumption of fish. The limitations and uncertainties of the approach are discussed including: (i) the uncertainties and particularities of the steady-state models used and (ii) the reliability of the approaches that are applied to derive critical limits for critical total dissolved metal concentrations in soil solution and surface water.
    [Show full text]
  • Ecology (Pyramids, Biomagnification, & Succession
    ENERGY PYRAMIDS & Freshmen Biology FOOD CHAINS/FOOD WEBS May 4 – May 8 Lecture ENERGY FLOW •Energy → powers life’s processes •Energy = ATP! •Flow of energy determines the system’s ability to sustain life FEEDING RELATIONSHIPS • Energy flows through an ecosystem in one direction • Sun → autotrophs (producers) → heterotrophs (consumers) FOOD CHAIN VS. FOOD WEB FOOD CHAINS • Energy stored by producers → passed through an ecosystem by a food chain • Food chain = series of steps in which organisms transfer energy by eating and being eaten FOOD WEBS •Feeding relationships are more complex than can be shown in a food chain •Food Web = network of complex interactions •Food webs link all the food chains in an ecosystem together ECOLOGICAL PYRAMIDS • Used to show the relationships in Ecosystems • There are different types: • Energy Pyramid • Biomass Pyramid • Pyramid of numbers ENERGY PYRAMID • Only part of the energy that is stored in one trophic level can be passed on to the next level • Much of the energy that is consumed is used for the basic functions of life (breathing, moving, reproducing) • Only 10% is used to produce more biomass (10 % moves on) • This is what can be obtained from the next trophic level • All of the other energy is lost 10% RULE • Only 10% of energy (from organisms) at one trophic level → the next level • EX: only 10% of energy/calories from grasses is available to cows • WHY? • Energy used for bodily processes (growth/development and repair) • Energy given off as heat • Energy used for daily functioning/movement • Only 10% of energy you take in should be going to your actual biomass/weight which another organism could eat BIOMASS PYRAMID • Total amount of living tissue within a given trophic level = biomass • Represents the amount of potential food available for each trophic level in an ecosystem PYRAMID OF NUMBERS •Based on the number of individuals at each trophic level.
    [Show full text]
  • Toxic Chemical Contaminants
    4 NaturalNatural RegionsRegions ofof thethe GulfGulf ofof MaineMaine TOXIC CHEMICAL CONTAMINANTS STATE OF THE GULF OF MAINE REPORT Gulf of Maine Census Marine Life May 2013 TOXIC CHEMICAL CONTAMINANTS STATE OF THE GULF OF MAINE REPORT TABLE OF CONTENTS 1. Issue in Brief ................................................................................................... 1 2. Driving Forces and Pressures .......................................................................4 2.1 Human .................................................................................................4 2.2 Natural .................................................................................................6 3. Status and Trends ..........................................................................................7 4. Impacts ........................................................................................................ 15 4.1 Biodiversity and Ecosystem Impacts ................................................ 15 4.2 Human Health ....................................................................................17 4.3 Economic Impacts ............................................................................. 18 5. Actions and Responses ............................................................................... 19 5.1 Legislation and Policy........................................................................ 19 5.2 Contaminant Monitoring ...................................................................20 6. Indicator Summary ......................................................................................23
    [Show full text]
  • Higher and More Variable Methylmercury Biomagnification
    Ecotoxicology and Environmental Safety 92 (2013) 191–198 Contents lists available at SciVerse ScienceDirect Ecotoxicology and Environmental Safety journal homepage: www.elsevier.com/locate/ecoenv Higher and more variable methylmercury biomagnification factors for floodplain than the contiguous river (South River, Virginia USA) Jincheng Wang a, Michael C. Newman a,n, Xiaoyu Xu a, Lian Liang b a Virginia Institute of Marine Science, College of William & Mary, P.O. Box 1346, Rt. 1208 Greate Road, Gloucester Point, VA 23062, USA b Cebam Analytical, Inc., 18804 North Creek Parkway, Suite 110, Bothell, WA 98011, USA article info abstract Article history: Extending previous trophic transfer studies of the mercury-contaminated South River watershed, Received 13 February 2012 predictive models were built for mercury biomagnification in floodplain food webs at two more Received in revised form locations (North Park and Grand Cavern). Four of five models built to date based on methylmercury and 25 April 2012 d15N met the a priori requirement for useful prediction (prediction r2E0.80). An additional factor Accepted 29 April 2012 included in models was organism thermoregulatory strategy (poikilothermy or homeothermy). The Available online 21 March 2013 methylmercury food web biomagnification factors (FWMFs, fold increase per trophic level) for the Keywords: North Park and Grand Cavern locations were 17.4 (95% CI of 9.5–31.6) and 6.2 (95% CI of 3.5–11.0) Mercury respectively. FWMF calculated in 2009 were 9.3 (95% CI of 5.4–16.2) for the Augusta Forestry Center Biomagnification and 25.1 (95% CI of 12.6–50.1) for Grottoes Town Park.
    [Show full text]
  • Lake Ouachita Fish Consumption Advisory Q&A
    Arkansas Department of Health 4815 West Markham Street ● Little Rock, Arkansas 72205-3867 ● Telephone (501) 661-2000 Governor Mike Beebe Nathaniel Smith, MD, MPH, Director and State Health Officer Lake Ouachita Mercury in Fish (MIF) Questions & Answers • How does the Arkansas Department of Health (ADH) decide when to issue a fish consumption advisory? ADH issues fish consumption notices when there are enough fish data to indicate that elevated levels of mercury have been reached. ADH works with the Arkansas Game and Fish Commission (AGFC), the Arkansas Department of Environmental Quality (ADEQ) and other state agencies in a Mercury in Fish (MIF) Taskforce. Typically, AGFC collects fish samples, ADEQ performs laboratory analysis of the fish tissue for mercury content, and ADH evaluates the fish data using a risk-based public health assessment method. When a specific fish species exceeds the action level of 1.0 part per million (ppm) mercury, theoretical calculations based on fish ingestion exposure to the mercury contamination are performed to determine potential risk for the public’s health. If a potential hazard is determined, ADH will issue a fish consumption advisory. • Where is this mercury coming from? Mercury comes from both naturally occurring and atmospheric depositions. An increase in mercury concentration in bodies of water is on the rise across the U.S. All 50 states have issued MIF advisories. Mercury is both naturally-occurring and man-made. Mercury contributions to water bodies are thought to be both from air deposition and from geologic formations. Mercury occurs naturally in the environment and is found in varying concentrations in soils and sediments throughout Arkansas.
    [Show full text]
  • Mercury in Fish – Background to the Mercury in Fish Advisory Statement
    Mercury in fish – Background to the mercury in fish advisory statement (March 2004) Food regulators regularly assess the potential risks associated with the presence of contaminants in the food supply to ensure that, for all sections of the population, these risks are minimised. Food Standards Australia New Zealand (FSANZ) has recently reviewed its risk assessment for mercury in food. The results from this assessment indicate that certain groups, particularly pregnant women, women intending to become pregnant and young children (up to and including 6 years), should limit their consumption of some types of fish in order to control their exposure to mercury. The risk assessment conducted by FSANZ that was published in 2004 used the most recent data and knowledge available at the time. FSANZ intends toreview the advisory statement in the future and will take any new data and scientific evidence into consideration at that time. BENEFITS OF FISH Even though certain types of fish can accumulate higher levels of mercury than others, it is widely recognised that there are considerable nutritional benefits to be derived from the regular consumption of fish. Fish is an excellent source of high biological value protein, is low in saturated fat and contains polyunsaturated fatty acids such as essential omega-3 polyunsaturates. It is also a good source of some vitamins, particularly vitamin D where a 150 g serve of fish will supply around 3 micrograms of vitamin D – about three times the amount of vitamin D in a 10 g serve of margarine. Fish forms a significant component of the Australian diet with approximately 25% of the population consuming fish at least once a week (1995 Australian National Nutrition Survey; McLennan & Podger 1999).
    [Show full text]
  • Fish and Shellfish Program NEWSLETTER
    Fish and Shellfish Program NEWSLETTER October 2018 This issue of the Fish and Shellfish Program Newsletter generally focuses on mercury. EPA 823-N-18-010 Recent Advisory News In This Issue Mercury and Fish Advisories Issued for Nine Recent Advisory News .............. 1 Waterways in Louisiana EPA News ................................ 3 On July 28, 2018, the Louisiana Departments of Health, Environmental Quality, and Other News ............................. 5 Wildlife and Fisheries issued a series of fish consumption advisories for nine bodies of Recently Awarded Research ... 15 water. These most recent advisories include one new warning and updates to eight previously issued warnings. Tech and Tools ...................... 16 Recent Publications .............. 17 Advisories are precautions and are issued when unacceptable levels of mercury are detected in fish or shellfish. Upcoming Meetings and Conferences ................... 19 Fish sampling is conducted by the Department of Environmental Quality. The Department of Health uses this data to determine the need for additional advisories or to modify existing advisories. Each advisory lists the specific fish, makes consumption recommendations, and outlines the geographic boundaries of the affected waterways. Because of mercury contamination, there are now fish consumption advisories for 48 waterways in Louisiana and one for the Gulf of Mexico. Louisiana fish consumption advisories are based on the estimate that the average resident eats four meals of fish per month (1 meal = ½ pound). Consuming more than this from local water bodies may increase health risks. This newsletter provides information only. This newsletter does not There are small amounts of mercury in the sediments of streams, lakes, rivers, and impose legally binding requirements oceans. Nearly all fish contain trace amounts of mercury.
    [Show full text]
  • Lead, Mercury and Cadmium in Fish and Shellfish from the Indian Ocean and Red
    Journal of Marine Science and Engineering Review Lead, Mercury and Cadmium in Fish and Shellfish from the Indian Ocean and Red Sea (African Countries): Public Health Challenges Isidro José Tamele 1,2,3,* and Patricia Vázquez Loureiro 4 1 Department of Chemistry, Faculty of Sciences, Eduardo Mondlane University, Av. Julius Nyerere, n 3453, Campus Principal, Maputo 257, Mozambique 2 Institute of Biomedical Science Abel Salazar, University of Porto, R. Jorge de Viterbo Ferreira 228, 4050-313 Porto, Portugal 3 CIIMAR/CIMAR—Interdisciplinary Center of Marine and Environmental Research, University of Porto, Terminal de Cruzeiros do Porto, Avenida General Norton de Matos, 4450-238 Matosinhos, Portugal 4 Department of Analytical Chemistry, Nutrition and Food Science, Faculty of Pharmacy, University of Santiago de Compostela, Santiago de Compostela, 15782 A Coruña, Spain; [email protected] * Correspondence: [email protected] Received: 20 March 2020; Accepted: 8 May 2020; Published: 12 May 2020 Abstract: The main aim of this review was to assess the incidence of Pb, Hg and Cd in seafood from African countries on the Indian and the Red Sea coasts and the level of their monitoring and control, where the direct consumption of seafood without quality control are frequently due to the poverty in many African countries. Some seafood from African Indian and the Red Sea coasts such as mollusks and fishes have presented Cd, Pb and Hg concentrations higher than permitted limit by FAOUN/EU regulations, indicating a possible threat to public health. Thus, the operationalization of the heavy metals (HM) monitoring and control is strongly recommended since these countries have laboratories with minimal conditions for HM analysis.
    [Show full text]
  • The Everglades Mercury Problem
    Everglades Interim Report Chapter 7: The Everglades Mercury Problem Chapter 7: The Everglades Mercury Problem Larry Fink, Darren Rumbold and Peter Rawlik Summary The Problem: Everglades sport fish have the highest average concentrations of mercury in Florida. Human health advisories remain in effect for a number of sport fish species throughout the Everglades, Big Cypress, and eastern Florida Bay. Federal and Florida water laws protect public health, wildlife populations, and the designated uses of a water body, including sport fishing. Until the advisories are lifted, sport fishers will not be able to freely consume the fish they catch. This denies them full enjoyment of the resource. The use of the sport fishery has thus been impaired. Studies are being conducted to determine whether the high concentration of mercury in Everglades fish are toxic to Everglades wildlife like wading birds. Adequacy of Standards: Data collected by the U.S. Environmental Protection Agency (USEPA) in the period 1993-1997 indicate that the Florida Class III numerical Water Quality Criterion for total mercury of 12 parts per trillion is not being exceeded anywhere in the Everglades canals and marshes. South Florida Water Management District (District, SFWMD) canal monitoring in 1997-1998 confirms this finding. These results have prompted DEP to reevaluate the mercury Water Quality Criterion. The DEP has determined that it is inadequate to protect recreational use and is funding studies to determine what criterion will protect human health and wildlife. Historical Inputs: A 1991-1992 study co-funded by the District, the DEP, and U.S. Geological Survey (USGS) found that the rate of mercury deposition from the atmosphere to the Everglades had increased about five-fold since the late 1800s.
    [Show full text]
  • The Influence of Ecological Processes on the Accumulation of Persistent Organochlorines in Aquatic Ecosystems
    master The influence of ecological processes on the accumulation of persistent organochlorines in aquatic ecosystems Olof Berglund DISTRIBUTION OF THIS DOCUMENT IS IKLOTED FORBGN SALES PROHIBITED eX - Department of Ecology Chemical Ecology and Ecotoxicology Lund University, Sweden Lund 1999 DISCLAIMER Portions of this document may be illegible in electronic image products. Images are produced from the best available original document. The influence of ecologicalprocesses on the accumulation of persistent organochlorinesin aquatic ecosystems Olof Berglund Akademisk avhandling, som for avlaggande av filosofie doktorsexamen vid matematisk-naturvetenskapliga fakulteten vid Lunds Universitet, kommer att offentligen forsvaras i Bla Hallen, Ekologihuset, Solvegatan 37, Lund, fredagen den 17 September 1999 kl. 10. Fakultetens opponent: Prof. Derek C. G. Muir, National Water Research Institute, Environment Canada, Burlington, Canada. Avhandlingen kommer att forsvaras pa engelska. Organization Document name LUND UNIVERSITY DOCTORAL DISSERTATION Department of Ecology Dateofi=" Sept 1,1999 Chemical Ecology and Ecotoxicology S-223 62 Lund CODEN: SE-LUNBDS/NBKE-99/1016+144pp Sweden Authors) Sponsoring organization Olof Berglund Title and subtitle The influence of ecological processes on the accumulation of persistent organochlorines in aquatic ecosystems Abstract Several ecological processes influences the fate, transport, and accumulation of persistent organochlorines (OCs) in aquatic ecosystems. In this thesis, I have focused on two processes, namely (i) the food chain bioaccumulation of OCs, and (ii) the trophic status of the aquatic system. To test the biomagnification theory, I investigated PCB concentrations in planktonic food chains in lakes. The concentra­ tions of PCB on a lipid basis did not increase with increasing trophic level. Hence, I could give no support to the theory of bio­ magnification.
    [Show full text]
  • Mercury Fate and Transport: Applying Scientific Research to Reduce the Risk from Mercury in Gulf of Mexico Seafood
    White Paper on Gulf of Mexico Mercury Fate and Transport: Applying Scientific Research to Reduce the Risk from Mercury in Gulf of Mexico Seafood February 2013 Gulf of Mexico Alliance Water Quality Team - Mercury Workgroup Gulf of Mexico Alliance, Water Quality Team GOMA Mercury Workgroup, White Paper Writing Team* David Evans National Oceanic and Atmospheric Administration Mark Cohen National Oceanic and Atmospheric Administration Chad Hammerschmidt Wright State University William Landing Florida State University Darren Rumbold Florida Gulf Coast University James Simons Texas A&M University, Corpus Christi Steve Wolfe Florida Institute of Oceanography/Gulf of Mexico Alliance *Note, document reviewed by Mercury Workgroup members and comments incorporated prior to release. Contents (hot linked, control-click on Contents entry to go to that location in document) Introduction .................................................................................................................................. 3 Section 1. Identification of at-risk groups................................................................................. 5 Research Needs and Approaches ............................................................................................... 6 Section 2. What Fish Species Have High Mercury Concentrations and Where Are They Found? .......................................................................................................................................... 8 Fish Harvests in the Gulf of Mexico .........................................................................................
    [Show full text]