The Year-Round Oyster Hatchery at Horn PointDon Meritt, Maryland Sea Grant Extension Shellfish Specialist
During spring and summer, the oyster hatchery at the Horn Point Laboratory is nothing less than hectic - during 2002, we produced x million eyed larvae and more than 70 million seed oysters. With the demand for seed increasing each year for restoration and research projects, we have added setting tanks and worked with the Oyster Recovery Partnership (ORP) in expanding the movement of seed oysters from the tanks to the field. For example, for years we filled mylar bags with shell for oysters to set on - rarely do we use these shell bags but now employ large stainless steel cages that enable us to move seed more efficiently. Oysters in the Chesapeake usually begin spawning sometime in June - however, at the Horn Point Laboratory, which is part of the University of Maryland Center for Environmental Science, we begin spawning oysters in the hatchery sometime in April. To do this, we have to provide adult oysters with environmental conditions early-on that mimic what they would experience in the wild. Conditioning OystersThe process begins with collecting selected broodstock - we try to choose oysters that have survived disease pressures, oysters from different regions or river systems, or oysters that may indicate other desirable features, such as fast growth. In the hatchery, we first examine them for their health and disease prevalence, then clean them of fouling organisms. We then place them in the HPL hatchery conditioning system - a conditioning system is a controlled environment for "ripening" oysters: while gonadal development is regulated by a number of factors, water temperature is primary. Once they are in the conditioning system, oysters are treated like royalty: they're provided with a constant supply of temperature-controlled river water, sometimes fed algae (especially if the natural spring algal bloom has not yet begun), cleaned twice each week (more if heavy fouling occurs) and monitored for growth, mortality and stage of ripeness. Though you will not see summer's pace and little may appear to be going on, nothing could be farther from the truth. We are actively growing algae for feeding broodstock, while storing reserves of algae for feeding larvae later on in the summer. We are also preparing the next group of oysters for introduction into the conditioning system. We attempt to have several groups of oyster broodstock staged, to be ready to spawn when we need them. However, we try to make sure that not all of them will have fully ripened at the same time but just ripen when they are needed. Oysters do not retain their gametes, so we employ this staging process (especially during the early spawning season) to keep freshly ripened oysters on hand. This process requires planning and coordination - if not done properly larval production can be slowed down. The expense of conditioning is considerable as a good deal of energy is required to heat river water to summer-like temperatures in April and May. The HPL hatchery operates with an open, or flow-through, system: using a series of titanium plate heat exchangers, water from the Choptank River is heated prior to its use - an automated valve system mixes the heated river water with ambient river water to produce the temperatures necessary for inducing gamete production. Depending on the time of year and the stage of ripeness of the oysters introduced into the system, this process can take a while to complete. For instance, oysters introduced from winter temperatures require about two months of conditioning before they are ready for spawning. Oysters collected from the wild later in the season may take less time for gametes to form, while those collected when ripe can be brought into the hatchery and spawned right away. It is advantageous to feed oysters when first brought in from winter conditions because algae are generally at a minimum in the Bay system. Once the spring algae bloom has begun, supplemental feeding from the algae we have grown is less critical. As water temperatures in the river warm, less heated river water is needed; generally by the middle of June, the system is switched over to a chiller which then cools Choptank river water and mixes it with the warm ambient water before it passes over the oysters. At this time, most oysters will be ripe or nearly ripe and the chilled water will prevent them from spawning naturally while in the system. While uncontrolled spawns can occur, reliable temperature control can greatly reduce their occurrence, which helps ensure a stable supply of ripe broodstock for the entire spawning season. Once again, a hatchery must have sufficient numbers of ripe oysters for broodstock or it is out of business. The dependability of the system in place to maintain strict temperature control on a twenty-four hour, seven-days a week basis is crucial. In most years it is possible to collect unspawned oysters from the wild until the end of June. After the Chesapeake's oysters have spawned naturally for the first time, ripe unspawned oysters are more difficult to find in the rivers. So it is important that we have enough ripe broodstock in the conditioning system to carry larval production through the remainder of the spawning season. During the past two years, we have had some success re-conditioning oyster broodstocks that had spawned at least once before. However, the numbers of oysters necessary for providing an equivalent amount of gametes increases greatly since not all oysters re-ripen at the same time - portions of the re-ripening broodstocks are often spawning naturally. We are investigating procedures that will help us more easily re-ripen brood oysters. In doing so, we should be able to significantly increase the length of time we're able to produce oyster larvae in the late summer or early fall. This will become more important as we move into the new Aquaculture and Restoration Ecology Laboratory later this season. Our current production season lasts approximately five months from April through August. This year, we've started our conditioning process early and hope to add a month; if we can add another month to the end of the season, we could produce 40 percent more oyster spat than we have in the past couple of years. Spawning TechniquesUnlike many hatcheries that spawn their broodstock by shucking the oysters and stripping eggs and sperm for fertilization, we employ a non-lethal method that allows us to induce spawning and collect the naturally-released gametes, so that the broodstock are available for subsequent spawns either later on in the same season or in subsequent seasons. Both stripping and non-lethal methods have advantages and disadvantages, depending on the goals. Strip spawning is advantageous when individual paired matings are desired. Research on the production of disease-resistant strains of oysters is carried out this way; strip spawning is also more reliable for research when using selected parents. Other hatcheries such as those on the west coast, which spawn the Pacific oyster Crassostrea gigas (this species is the basis of the industry there), use this method to produce the bulk of their larvae. In our mass spawning approach at the Horn Point hatchery, we place 25 to 400 oysters in flowing heated river water to induce natural spawning. Often stimulated with gametes from oysters that we do shuck, this method has successfully produced billions of eggs and sperm. We collect eggs and sperm, combine them in the proper ratio for fertilization and then distribute the new larvae to tanks where they will feed for two to three weeks. Salinity levels vary from year to year, depending on rainfall - we need a minimum of 8 parts per thousand, preferably above 10 ppt at 25ºC. Because natural algae at our location in the Choptank River rarely provide larval oysters with adequate nutrition, we produce all of the algae they will need. Larval tanks are drained at least three times a week, the tanks cleaned and refilled with filtered river water, and the larvae culled and examined microscopically for problems - new algae are added to provide for larval nutrition. During the three weeks that larvae are feeding, they are also developing physiologically and readying for metamorphosis. Under the microscope you can observe a foot and an eye spot - this is an indication that they are ready to metamorphose from a free-swimming larvae to an attached spat. This process is referred to as settlement or setting and, physiologically, is very stressful on the larvae. We collect "eyed" larvae and move them to tanks at Horn Point or send them to other labs or organizations, which will set the larvae in tanks at their locations. The majority of larvae at Horn Point are set on oyster shell that the Maryland Department of Natural Resources provides. Other substrate is also being used elsewhere, with varying degrees of success, for example, concrete reef balls and limestone marl rock. Once settlement is completed, the spat (as they are now called) are typically removed from the setting tanks and placed in a shallow-water nursery near the Horn Point Laboratory pier. At this stage they are the size of a grain. After a few weeks, they will grow to almost an inch - they are much hardier and easier to transport. They are then ready for deployment to outplanting sites throughout the Bay. The Oyster Recovery Partnership, a non-profit organization in Maryland that has become a key coordinator in many restoration efforts, works with Maryland DNR, which supplies shell for stabilizing bottom grounds and identifies state sanctuary sites. ORP has also established wide-ranging partnerships with Maryland Watermen, federal agencies, non-profit organizations and community groups in oyster planting projects throughout Maryland's portion of the Bay. Public bottom grounds in the state are designated as sanctuaries which are never to be harvested, managed reserves which are to be harvested under conditions designed to provide maximum economic benefit to the commercial oystermen, and traditional harvest bars which are part of the current oyster fishery. Research has been underway to determine the most effective planting strategies of these grounds for "smart" restoration of oyster populations. New HatcheryThe new hatchery facility at Horn Point in the Aquaculture and Restoration Ecology Laboratory will greatly increase out ability to produce oyster spat. It will house state-of-the-art temperature controls that have design features based on 30 years of experience at the HPL hatchery. We will be able to hold more than two-and-a-half times the broodstock that we can hold now in a controlled temperature laboratory; we will also have a second broodstock holding facility for use in the re-conditioning process. The recirculating water system will enable us to simulate winter conditions so we can better mimic conditions for out-of-season spawning. A state-of-the-art quarantine lab will allow us to work on species without the risk of animals escaping in the wild. Other improvements and the expanded size of this facility will greatly increase our ability to produce more and higher quality oyster spat for use in out research programs and with our partners in Bay restoration. For more information about the Horn Point Laboratory hatchery, see www.hpl.umces.edu/facilities/oysters.html. In addition to photographs that detail hatchery practices, there are video clips of oyster spawning, eyed larvae and oyster setting. RESEARCH UPDATENew Potential Feed for TilapiaSteven Hughes, University of Maryland Eastern ShoreDelmarva poultry farms generate an immense volume of waste litter - while a great deal of this litter has been spread on Eastern Shore farmland, recent studies at the University of Maryland Eastern Shore's Aquaculture Research and Demonstration Project indicate that litter could have a surprisingly different use as an inexpensive source of fish food. The investigation consisted of studies with hybrid tilapia that compared the digestibilities of pelleted feeds containing either varying percentages of poultry litter (PPL) or no poultry litter and a feeding trial to determine the impact of feeding PPL on the growth and feed conversion of these fish. The first experiment assessed the digestibility of both nitrogen (protein) and phosphorus in the PPL. Indications were that both nutrients are readily digested by tilapia: nitrogen digestibility values for PPL of 86-89% were excellent and comparable to literature values for wheat products, while phosphorus digestibility values of 84-87% were also very good. These data supported the initial premise that tilapia would be able to use PPL as a significant feed ingredient. The second experiment was designed to determine the presence or absence of the liver enzyme uricase in tilapia. This enzyme would be essential to the long-term use of PPL for tilapia because the PPL contains relatively high levels of uric acid from the poultry waste. Without an active liver uricase system, the uric acid from the PPL would build up in the blood and tissues of the tilapia and rapidly become toxic. Our data indicated that tilapia have an active liver uricase system and that the activity is intermediate when compared with data from other fish species. In a third experiment, in which we manufactured tilapia feeds but replaced wheat middlings with PPL, preliminary data indicate that the fish utilized PPL extremely well. PPL was able to completely replace wheat middlings (which comprised almost 20 percent of the feed) and there was no measurable difference in either weight gain or condition between fish fed this feed or the diet containing middlings. The impact of PPL feed on liver uricase levels was highly variable, though generally it had no significant effect on the levels of this enzyme. These additional data would indicate that tilapia are having no physiological problems with the uric acid in the PPL. The results of this research support the premise that pelleted poultry litter can be used in the tilapia feeds in significant quantities and that further research to determine the most economical feeding levels is warranted. For more information, contact Steve Hughes at sghughes@mail.umes.edu RESEARCH UPDATE
Blue Crabs May Benefit From AlgaeBarbara GarbiniExperiments to determine a more sophisticated understanding of the basic biology, nutritional requirements and water quality needs of the blue crab have been underway for two years at the Center of Marine Biology, part of the University of Maryland Biotechnology Institute. The goal of these studies is to optimize growth and reduce mortality of hatchery-reared crabs destined for research studies on enhancing of the Chesapeake Bay's blue crab stocks. The feasibility of enhancement itself may depend on advancements in large-scale, indoor, closed system hatchery and nursery aquaculture technologies for producing young crabs. Research studies involving growth and nutrition of blue crabs have shown that juvenile crabs require refuge from both predation and cannibalism in a sea grass habitat. In an aquaculture setting, cannibalism can be reduced with the introduction of a single-size class of crab. While analyses conducted of crab stomach contents at all stages of development indicate that crabs consume microscopic algae, it is not clear whether the algae or their associated bacteria provide additional nutrition to the developing crab. In an experiment funded by the COMB blue crab hatchery program and Maryland Sea Grant, 120 juvenile blue crabs within a single-size class (1.5 - 2.0 cm) were divided into several tanks with artificial seagrass and fed supplementary diets of microscopic algae, bacteria or a combination of both. The goal of the experiment was to determine if the presence of algae or bacteria could provide additional nutrition for growth and improve survival rates of the crabs during the juvenile stages of development, while providing for improved water quality in a closed system. After 28 days, the overall mortality rate of the 120 juvenile crabs was 43 percent. Crabs fed large amounts of bacteria had a significantly higher mortality rate of 77 percent, became lethargic and soft, and in some cases failed to molt. Crabs fed supplemental diets of microscopic algae had a significantly higher daily rate of wet weight growth (when compared to a control group), which suggests that algae can play a role in nutrition in the juvenile stage of development. Supplements of both algae and bacteria did not show a significantly higher rate of growth, an indication that the bacterium does not provide additional nutrition and is most likely detrimental to the overall health of the crab. All tanks that contained microscopic algae maintained higher water quality where nitrate, nitrite and ammonia levels were low throughout the experiment. This experiment implies that the addition of microscopic algae along with artificial sea grass cover may provide additional nutrition to the juvenile blue crab, increase its daily growth rate and significantly improve water quality in a closed aquaculture system. The use of microscopic algae could have another benefit as well, an economical one. While Artemia napollii and commercial feeds are routinely used in the rearing of larval and juvenile crabs and are a good source of nutrition, they are expensive for large-scale operations. Inexpensive supplemental diets such as microscopic algae that can be grown on artificial sea grass, and that can support and increase growth through the juvenile stages of development, will be beneficial for aquaculture facilities. Barbara Garbini is a graduate student at Hood College; she is working under the direction of Dr. Moti Harel, Center of Marine Biotechnology, and Dr. Dan Terlizzi, Maryland Sea Grant Water Quality Specialist. For more information on blue crab research at COMB, contact Steve Berberich at 301-990-4804 or berberic@umbi.umd.edu. For details, see www.umbi.umd/~comb BOOK REVIEWFarming Shellfish - Covering All the BasesDon Webster, Maryland Sea Grant Extension Program, Eastern Shore Agent
Molluscan Shellfish Farming, Brian E. Spencer, Blackwell Science, Fishing News Books (Iowa State Press, a Blackwell Publishing Company), Ames, Iowa. 2002. 272 pp. $96.99. www.iowastatepress.comI have several shelves of publications from Fishing News Books. This United Kingdom publishing house has produced useful reference texts on fisheries and aquaculture topics for decades - Molluscan Shellfish Farming will now be found on my ready reference shelf. The book derives from the Buckland Lecture, a prestigious series first begun in 1930 for addressing fisheries related topics. Brian Spencer's lecture forms the basis of the book's first chapter, "Bivalve cultivation in the UK: structuring influences." Since U.S. law is largely based upon British common law concepts, the discussion of legislation and rights to grow and harvest shellfish are similar in many respects and should be interesting to the legal novice. The chapter also covers the experience of uncontrolled imports of shellfish seed to the UK after the flat oyster industry collapsed in the 1900s. Pests accompanied some seed and finally led to control orders in 1974 that have aided in minimizing the spread of unwanted organisms. The experience of the UK in introducing several species of non-native bivalves was similarly intriguing. These were brought in under quarantine and information is provided on the species, origin, and fate of the animals. Among those are the Pacific and American (Eastern) oyster, and the Manila clam. Protocols developed under the auspices of the International Council for the Exploration of the Seas (ICES) to assess the impact of non-native introductions are referred to throughout the volume. With the current examination of the efficacy of the Suminoe oyster Crassostrea ariakensis in mid-Atlantic waters, these issues are especially relevant. They have, of course, been faced before in other countries. "Probably the most contentious issue with introducing non-native species is associated with their breeding potential," writes Spencer. "For the past 30 years, it has been (UK) government policy not to introduce a species where there is a risk of it becoming established and creating self-sustaining populations." The government seeks to protect the environment while all possible effort is made to support a healthy aquaculture industry. Indeed, Spencer makes clear the need for aquaculture in addressing a primary shortcoming of reliance on natural reproduction, that of irregularity of spatfall. The chapter on the "General Biology of Bivalves with Respect to Cultivation," provides an overview of the natural functions of commercially important shellfish. While certainly not inclusive of all available information, Spencer gives basic data on the topic. Covering many species, his writing is concise writing and includes appropriate diagrams and bulleted descriptions of techniques that provide a clear understanding of the methods he describes. When I read near the end of the chapter this sentence - "Successful hatchery production of larvae and spat is related more to the skill and experience of the staff than to the excellence of the facilities and equipment" - I thought of the late Max Chambers and his original hatchery near Nanticoke, Maryland. (see "A Man and His Ideas," www.mdsg.umd.edu/Extension/Aquafarmer/Summer01.html#4). The chapters on shellfish cultivation techniques make the book especially useful; the text is enhanced with photographs that illustrate grow-out techniques in use around the world. These techniques suggest a basic lesson of successful shellfish production methods: they must be adapted to local hydrological features. High, three-dimensional grow-out methods, for example, may be more effective in areas where there is high tidal amplitude; lower, more spread-out methods are generally better in areas where tidal fluctuations are low. Spencer also includes grow-out equipment from many nations around the world, from bottom culture in the Pacific Northwest to rotating cylinders used in Australia. It is clear that Spencer has a broad range of knowledge in mollusk culture. There are individual chapters on oysters, clams, mussels, scallops, and abalone culture. (While not a mollusk, abalone is included because it is a shellfish and a significant body of knowledge exists on its culture. These chapters are well planned and well written. There are diagrams of culture methods along with the photographs of actual deployments. Spencer provides historical information about shellfish culture in these as well, showing that mankind has had a fascination with growing mollusks for many centuries. His characterizations of Asian rock and stick culture show that sophisticated equipment is not necessarily required for cultivation - only human ingenuity. Of course, suitable laws or lack of prohibitions on growing areas and methods are critical for success as well. This is a primary reason why shellfish aquaculture in Maryland has had such a difficult history. These chapters, as with all others in the book, are well referenced and include relevant literature citations. An important topic in any type of aquaculture is the control of predators. This is a basic function of culture along with preventing disease, controlling mortality, enhancing growth, and optimizing quality. Spencer's discussion on predator control and exclusion methods is wide-ranging. While he recognizes bird and fish predation, he focuses a great deal of attention on controlling the impact of crabs. He describes exclusion devices used on mollusk farms as a primary means of protection and gives examples of their use. He also discuses chemical control methods along with the more usual mechanical methods and he provides the statutory powers in the UK for these. In a chapter on site selection for bivalve aquaculture, Spencer notes that it is "a multi-faceted problem that requires an assessment of a range of information to ensure that a new business venture stands a good chance of success." Too many businesses in Maryland and elsewhere have found this out too late to keep from failing. He gives a concise overview of site selection that summarizes the physical, biological, and legal information that must be gathered by the prospective culturist before a site can be judged as viable. As always, Spencer provides a range of topics that cover many aspects of important site criteria. The last chapter covers important information on the "Processing of Live Bivalves for Consumption." It has been known for decades that shellfish are susceptible to bacterial pollution and can be significant sources of disease in humans. Sanitation programs have been developed to ensure that only quality seafood reaches the marketplace. Spencer gives a history of the development of depuration facilities, providing information on their design and operation to ensure that cleansed shellfish reach the consumer. He compares the advantages and disadvantages of depuration methods according to a range of criteria. These include capital and operating costs, installation and maintenance costs, dose and contact time, and toxicity to the shellfish themselves. While depuration is frequently looked upon with disdain in the United States, this discussion provides a glimpse into modern processing methods used in European markets to assure consumer health. Molluscan Shellfish Farming is an excellent addition to any shellfish culturist's reference collection. It should receive widespread distribution and use in future years. It certainly meets the high standards set by Fishing News Books and its parent company, Blackwell Science. Country of Origin Labeling Coming to Your Seafood CounterDoug Lipton, Marine Economic Specialist, Maryland Sea Grant Extension
The next time you buy fish or shellfish or crab, see if the country of origin is identified, or whether the product was The 2002 Farm Bill, the omnibus legislation governing federal agriculture programs for the next six years, contains a provision requiring the Secretary of Agriculture to develop mandatory regulations governing country of origin labels for certain food products including wild fish and farm-raised seafood. These regulations will need to be finalized by September 30, 2004, although voluntary guidelines for labeling are currently in place. The cost of these new requirements - referred to as COOL (Country of Origin Labeling) Seafood - may be costly to retailers and their suppliers as they will have to keep track of the different sources of their products. (Restaurants and other types of food service establishments will be exempt from labeling requirements.) Each business in the marketing chain will have to keep records and certify to the business to which they sell as to the country of origin of the product they are supplying. So who is likely to benefit from these new regulations? The simple answer is consumers and domestic producers. Consumers will now have more information about the seafood they are purchasing. As E.F. Golan et al. discussed in "Economics of Food Labeling" (Journal of Consumer Policy. 2001. 24:177-184), there are three scenarios regarding how this information may affect consumers: (1) consumers may not care about the country of origin, (2) they may prefer the imported product, or (3) they may prefer the domestic product. Which of these scenarios holds may depend on the specific fish or shellfish product being purchased. However, if consumers do prefer the domestic product, then domestic producers will benefit from the greater demand and market share. In a study of nutrition labeling using the 1987-88 Nationwide Food Consumption Survey, Wang et al. in "Consumer Utilization of Food Labeling as a Source of Nutrition Information" (The Journal of Consumer Affairs. 1995. 29:368-380) found that about 45 percent of households used food labels for nutrition information. They also found that the likelihood of a household using nutrition label information in their purchasing decision depended on factors such as income, level of education, geographic location and other socio-demographic factors. Interestingly, consumers were more likely to use nutrition labels when they were more aware of the health effects of food consumption. For example, people who were trying to limit their fat intake were more likely to use the labels in the purchase decision. The study on the use of nutrition labels has important implications for the effectiveness of country of origin labeling for seafood. If consumers are aware of quality or other differences between domestic and imported seafood, or between wild and farm-raised seafood, then the country of origin labeling requirement is more likely to have an impact on their purchase decision. Thus, there are opportunities for consumer education and marketing to capitalize on this new information the consumer will have at the seafood counter. For more information on COOL, contact Doug Lipton at dlipton@arec.umd.edu Acid Mine Drainage in the Chesapeake WatershedMatt HallThe Potomac River is the second largest river feeding the Chesapeake Bay (the Susquehanna is the largest) - flowing from its head waters in West Virginia through Garrett County in far western Maryland, it is fed by numbers of tributary streams. Lostland Run is one such stream. Fly fishermen are out there at the beginning of Spring casting their lines for stocked rainbow trout or cryptic native brook trout; hikers are out there as well traversing the backwoods trails. Unbeknownst to many, abandoned coal mines leach a steady stream of acid into Lostland Run's upper reaches. Were it not for a tall metal tower positioned over the south prong of Lostland, fishermen would not likely be casting their lines - there would probably be no trout to catch. Referred to as a doser by the Maryland Bureau of Mines, the tower steadily spills limestone into the water below, thereby buffering the stream against the acid it collects flowing past the defunct coal mines above. "Acid mine drainage (AMD) is the number one water quality problem in the Appalachians" says Ray Morgan, a Professor at the Appalachian Laboratory, part of the University of Maryland Center for Environmental Science in Frostburg. "It can destroy streams. Iron, manganese, and aluminum are transported downstream and the water is unfit for consumption and industrial or municipal use." Morgan has worked for most of his career on water quality issues in Maryland and West Virginia watersheds. He has also monitored reclamation efforts in several western Maryland watersheds, including the doser on water quality of Lostland Run. High levels of acidity from abandoned mines are lethal to stream-dwelling organisms up and down the food chain - from large fish to small invertebrates. The metallic ions associated with AMD can also reach toxic levels. Because some species are more tolerant of lower pH levels (acidity) and metallic ion concentration, they can come to dominate biota that are not so tolerant, leading to declines in biological diversity. Not only are biological impacts acute at the source of discharges, but chronic effects are evident as well, Morgan says. This is because compounds like iron precipitate ("yellowboy") may be retained in soil layers and rock below a stream channel (called the hyporheic zone) for many years. According to a 1997 report from the U.S. Environmental Protection Agency, a large area of the Chesapeake drainage is impacted by acid mine drainage - the Susquehanna watershed, lying as it does in areas of rich anthracite coal beds, is a primary example. The bituminous coal region encompasses large swathes of the West Branch Susquehanna system in Pennsylvania and the North Branch of the Potomac River and its tributaries in West Virginia and Maryland. (Lostland Run feeds the North Branch.) According to the report, acid mine drainage affects 1100 miles in 158 streams in the Chesapeake drainage. This includes a majority of the central and western sections of the Bay watershed. So what can be done about acid mine drainage? A number of abatement techniques, in addition to doser technology for releasing limestone into stream flow, are in use throughout the watershed. These include treating the discharges directly, reclaiming abandoned mine lands, regrading and revegetating mine refuse piles, sealing abandoned mines, and remining abandoned mine sites. Reclamation efforts also include the construction of wetlands that can act as filters for contaminated run-off. While all of these measures are being used in the Chesapeake watershed, there have been varying degrees of success. Joe Mills is an acid remediation specialist with the Maryland Department of the Environment's Bureau of Mines in Frostburg. He says that since 1995, Maryland's permitting system provides safeguards for preventing contaminated run-off from currently operating mines. However, he adds, "our biggest priority now is locating pre-law, abandoned mines that are discharging acid. We have located hundreds of these in western Maryland, but there are probably hundreds more. This project will take years." Connie Lyons, also of the Bureau of Mines, agrees and takes the issue a step further. "Our most difficult problem is the variability in abandoned mines. Damage from acid mine drainage depends on the size of the mine and the size of the receiving stream. Sometimes, a mine may only discharge once a year, but that may be enough to damage a stream ecosystem and make recovery difficult." Despite these challenges, both Mills and Lyons point to the success of the Bureau's reclamation efforts. Six dosers, including the one on Lostland Run, pump tons of limestone and limestone derivatives into tributaries of the severely impacted North Branch of the Potomac River. Prior to their installation in 1992 and 1993, waters flowing from several abandoned mine sites kept the North Branch at an acidic pH of between 3.24 (severely acidic) and 7.0 (neutral), depending on water flow. Fish populations were so impacted that fishing was virtually non-existent - game and non-game fishes experienced high mortality or drastically-reduced reproduction in the acidic water. Because of the dosers, 35 miles of Potomac headwater have been reclaimed to a fishable condition, including eight miles of "trophy" trout stream below Jennings-Randolph Lake. The dosers, says Mills, have been raising pH and reducing acid-related mineral precipitation, while operating at relatively low cost. "In 1994, we spent $94,000 to run four dosers," he says. "In 2002, $67,126 was spent to operate seven dosers." A recent economic study estimated that recreational fishing areas see roughly twelve dollars in return (in fishing license fees, bait and tackle sale, local hotel and campground fees, etc.) for every dollar spent. With the reduction in doser operating costs, potential revenue per dollar spent is doubled." Though the cost reduction is attributable mainly to the use of less refined limestone, Mills says, it produces the same neutralizing effect as the high-grade compound. Given the success in Maryland so far in treating the impacts of acid mine drainage, we're just at the beginning, Mills says - many sources still must be located and monitored in order to determine the best strategies for eliminating or simply minimizing their impacts on living organisms. Without the research that has gone into developing current techniques for ameliorating these impacts, many of the Chesapeake's headwater streams would be virtually sterile environments. For more information, visit the Maryland Department of Environment at www.mde.state.md.us/Programs/WaterPrograms/MiningInMaryland/MDAcidDrainage/index.asp. Matthew R. Hall is a Research Statistician in the Tidewater Ecosystem Assessment Division of the Maryland Department of Natural Resources.
What Is Acid Mine Drainage?Matt HallWhether drilling deep shafts to reach coal or strip mining near the surface, coal seams and surrounding bedrock are exposed to oxygen and water. Most coal seams in the Chesapeake drainage are high in iron disulfide (FeS2), commonly known as pyrite. When pyrite is exposed to air and water, oxidation reactions produce sulfuric acid (H2SO4) and ferrous iron ions (Fe2+) in a water solution. This chemical reaction decreases the pH of the solution by contributing more hydrogen ions - the more hydrogen ions present in solution, the lower the pH is and the more acidic the solution (pH below 7.0 is acidic and above 7.0 basic). The ferrous iron is then oxidized to ferric iron (Fe3+). These reactions do not take place spontaneously but are catalyzed by bacteria present in the underground water. Sulfuric acid is the most toxic product of these reactions and will affect most stream organisms. Ferric iron ions in solution are also acidic and cause pyrite to dissolve, producing more sulfuric acid and iron ions. As these products move into a stream, ferric iron ions precipitate out of solution as solid iron oxide FE(OH)3 or "yellowboy." Yellowboy forms orange-red deposits in streams leaving a telltale sign of acid mine drainage contamination. The Maryland Bureau of Mines and other regulatory agencies combats this contamination by treating stream water with limestone (CaCO3) or its derivatives: limestone reacts directly with sulfuric acid, tying up free hydrogen ions and thus raising the pH of the water, which reduces its acidity. This process is known as neutralization and is quite effective for removing acidity from stream water. (Source: S.E. Manahan, Environmental Chemistry, PWS Publishers, Boston, 1984.)
Partnership to Develop Integrated
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Maryland Sea Grant Extension Program
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Douglas Lipton Coordinator and Marine Economics Specialist |
(301) 405-1280 |
dlipton@arec.umd.edu |
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Vicky Carrasco Coastal Communities Specialist |
(301) 405-5809 |
vcarrasco@arec.umd.edu |
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Adam Frederick Environmental Education Specialist |
(410) 234-8850 |
frederic@mdsg.umd.edu |
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Andrew M. Lazur Finfish Aquaculture Specialist |
(410) 221-8474, 8496 |
alazur@hpl.umces.edu |
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Gayle Mason-Jenkins Seafood Nutrition Specialist |
(410) 651-6212 |
gmjenkins@mail.umes.edu |
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Don Meritt Shellfish Aquaculture Specialist |
(410) 221-8475 |
meritt@hpl.umces.edu |
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Tom Rippen Seafood Technology Specialist |
(410) 651-6636 |
terippen@mail.umes.edu |
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Jackie Takacs Marine Agent |
(410) 326-7356 |
takacs@cbl.umces.edu |
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Dan Terlizzi Water Quality Specialist |
(410) 234-8837 |
dterlizz@umd.edu |
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Don Webster Marine Agent |
(410) 827-8056 ext. 127 |
dwebster@umd.edu |
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Denise Wist Administrative Assistant |
(301) 405-6935 |
dwist@arec.umd.edu |
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The MARYLAND AQUAFARMER Newsletter is produced quarterly each year by the Cooperative Extension Service, University of Maryland, College Park with support from the Maryland Sea Grant College Program and is issued as a public service for the aquaculture industry. Annual subscriptions are free of charge. |
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Aquafarmer Editor |
Maryland Aquafarmer index Last modified August 04, 2003 http://www.mdsg.umd.edu/Extension/Aquafarmer/Spring03.html |
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Issued in furtherance of Cooperative Extension work, acts of May 8 and June 30, 1914, in cooperation with the U.S. Department of Agriculture, University of Maryland, College Park, and local governments. Thomas A. Fretz, Director of Cooperative Extension Service, University of Maryland, College Park. The Maryland Sea Grant Extension Program is a joint effort of the Cooperative Extension Service and the Maryland Sea Grant College, supported in part by NOAA Office of Sea Grant, Department of Commerce. The University of Maryland is equal opportunity. The University's policies, programs, and activities are in conformance with pertinent Federal and State laws and regulations on nondiscrimination regarding race, color, religion, age, national origin, sex, and disability. Inquiries regarding compliance with Title VI of the Civil Rights Act of 1964, as amended; Title IX of the Educational Amendments; Section 504 of the Rehabilitation Act of 1973; and the Americans With Disabilities Act of 1990; or related legal requirements should be addressed to the Director of Personnel/Human Relations, Office of the Dean, College of Agriculture and Natural Resources, Symons Hall, College Park, MD, 20742 |