Name: laboratory estimation of net trophic transfer efficiencies of pcb congeners to lake trout (salvelinus namaycush) from its prey
Uploaded: 2014-08-29T13:00:00
Description: Watch this Scientific Journal Video about Laboratory Estimation of Net Trophic Transfer Efficiencies of PCB Congeners to Lake Trout Salvelinus namaycush from Its Prey at JoVE.com

This work was funded, in part, by the Great Lakes Fishery Commission and the Annis Water Resources Institute. Use of trade, product, or firm names does not imply endorsement by the U. S. Government. This article is Contribution 1867 of the U. S. Geological Survey Great Lakes Science Center.

1. Laboratorie Experiment <ol><li> Skaff byttedyr fisk å bli matet til rovfisk under forsøket. Fortrinnsvis er disse byttedyr fisken skal fanges opp i felten, frosset og lagret ved omtrent -30 ° C. Vurdere kommersielle fisket som en potensiell kilde for byttedyr fisk. </li><li> Introduser rovfisk inn i laboratorietanker som skal anvendes for forsøket. Opp til 15 rovfisk har blitt introdusert inn i hver av 870-L tanker, og opp til 30 rovfisk har blitt introdusert inn i hver av 2380-L-tanker i tidligere studier <sup...

<ol>
	<li>Madenjian, C. P., Carpenter, S. R., Rand, P. S. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Why+are+the+PCB+concentrations+of+salmonine+individuals+from+the+same+lake+so+highly+variable?.">Why are the PCB concentrations of salmonine individuals from the same lake so highly variable?.</a> Canadian Journal of Fisheries and Aquatic Sciences. 51 (4), 800-807 (1994).</li><li>Madenjian, C. P., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Net+trophic+transfer+efficiency+of+PCBs+to+Lake+Michigan+coho+salmon+from+their+prey.">Net trophic transfer efficiency of PCBs to Lake Michigan coho salmon from their prey.</a> Environmental Science and Technology. 32 (20), 3063-3067 (1998).</li><li>Thomann, R. V. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Bioaccumulation+model+of+organic+chemical+distribution+in+aquatic+food+chains.">Bioaccumulation model of organic chemical distribution in aquatic food chains.</a> Environmental Science and Technology. 23 (6), 699-707 (1989).</li><li>Calabrese, E. J., Baldwin, L. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Performing ecological risk assessments. , (1993).</li><li>Madenjian, C. P., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Variation+in+net+trophic+transfer+efficiencies+among+21+PCB+congeners.">Variation in net trophic transfer efficiencies among 21 PCB congeners.</a> Environmental Science and Technology. 33 (21), 3768-3773 (1999).</li><li>Jackson, L. J., Schindler, D. E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Field+estimates+of+net+trophic+transfer+of+PCBs+from+prey+fishes+to+Lake+Michigan+salmonids.">Field estimates of net trophic transfer of PCBs from prey fishes to Lake Michigan salmonids.</a> Environmental Science and Technology. 30 (6), 1861-1865 (1996).</li><li>Gobas, F. A. P. C., Muir, D. C. G., Mackay, D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Dynamics+of+dietary+bioaccumulation+and+faecal+elimination+of+hydrophobic+organic+chemicals+in+fish.">Dynamics of dietary bioaccumulation and faecal elimination of hydrophobic organic chemicals in fish.</a> Chemosphere. 17 (5), 943-962 (1988).</li><li>Madenjian, C. P., O&#8217;Connor, D. V., Rediske, R. R., O&#8217;Keefe, J. P., Pothoven, S. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Net+trophic+transfer+efficiencies+of+polychlorinated+biphenyl+congeners+to+lake+whitefish+(Coregonus+clupeaformis)+from+their+food.">Net trophic transfer efficiencies of polychlorinated biphenyl congeners to lake whitefish (Coregonus clupeaformis) from their food.</a> Environmental Toxicology and Chemistry. 27 (3), 631-636 (2008).</li><li>Isosaarl, P., Kiviranta, H., Lie, &. #. 2. 1. 6. ;., Lundebye, A. K., Ritchie, G., Vartiainen, T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Accumulation+and+distribution+of+polychlorinated+dibenzo-p-dioxin,+dibenzofuran,+and+polychlorinated+biphenyl+congeners+in+Atlantic+salmon+(Salmo+salar).">Accumulation and distribution of polychlorinated dibenzo-p-dioxin, dibenzofuran, and polychlorinated biphenyl congeners in Atlantic salmon (Salmo salar).</a> Environmental Toxicology and Chemistry. 23 (7), 1672-1679 (2004).</li><li>Buckman, A. H., Brown, S. B., Hoekstra, P. F., Solomon, K. R., Fisk, A. T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Toxicokinetics+of+three+polychlorinated+biphenyl+technical+mixtures+in+rainbow+trout+(Oncorhynchus+mykiss).">Toxicokinetics of three polychlorinated biphenyl technical mixtures in rainbow trout (Oncorhynchus mykiss).</a> Environmental Toxicology and Chemistry. 23 (7), 1725-1736 (2004).</li><li>Burreau, S., Axelman, J., Broman, D., Jakobsson, E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Dietary+uptake+in+pike+(Esox+lucius)+of+some+polychlorinated+biphenyls,+polychlorinated+naphthalenes+and+polybrominated+diphenyl+ethers+administered+in+natural+diet.">Dietary uptake in pike (Esox lucius) of some polychlorinated biphenyls, polychlorinated naphthalenes and polybrominated diphenyl ethers administered in natural diet.</a> Environmental Toxicology and Chemistry. 16 (12), 2508-2513 (1997).</li><li>Madenjian, C. P., DeSorcie, T. J., Stedman, R. M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Ontogenic+and+spatial+patterns+in+diet+and+growth+of+lake+trout+in+Lake+Michigan.">Ontogenic and spatial patterns in diet and growth of lake trout in Lake Michigan.</a> Transactions of the American Fisheries Society. 127 (2), 236-252 (1998).</li><li>Paterson, G., Whittle, D. M., Drouillard, K. G., Haffner, G. D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Declining+lake+trout+(Salvelinus+namaycush)+energy+density:+are+there+too+many+salmonid+predators+in+the+Great+Lakes?.">Declining lake trout (Salvelinus namaycush) energy density: are there too many salmonid predators in the Great Lakes?.</a> Canadian Journal of Fisheries and Aquatic Sciences. 66 (6), 919-932 (2009).</li><li>Madenjian, C. P., O&#8217;Connor, D. V., Nortrup, D. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+new+approach+toward+evaluation+of+fish+bioenergetics+models.">A new approach toward evaluation of fish bioenergetics models.</a> Canadian Journal of Fisheries and Aquatic Sciences. 57 (5), 1025-1032 (2000).</li><li>Madenjian, C. P., Pothoven, S. A., Kao, Y. C. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Reevaluation+of+lake+trout+and+lake+whitefish+bioenergetics+models.">Reevaluation of lake trout and lake whitefish bioenergetics models.</a> Journal of Great Lakes Research. 39 (2), 358-364 (2013).</li><li>Madenjian, C. P., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Evaluation+of+a+lake+whitefish+bioenergetics+model.">Evaluation of a lake whitefish bioenergetics model.</a> Transactions of the American Fisheries Society. 135 (1), 61-75 (2006).</li><li>Madenjian, C. P., O&#8217;Connor, D. V., Chernyak, S. M., Rediske, R. R., O&#8217;Keefe, J. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Evaluation+of+a+chinook+salmon+(Oncorhynchus+tshawytscha)+bioenergetics+model.">Evaluation of a chinook salmon (Oncorhynchus tshawytscha) bioenergetics model.</a> Canadian Journal of Fisheries and Aquatic Sciences. 61 (4), 627-635 (2004).</li><li>Madenjian, C. P., David, S. R., Rediske, R. R., O&#8217;Keefe, J. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Net+trophic+transfer+efficiencies+of+polychlorinated+biphenyl+congeners+to+lake+trout+(Salvelinus+namaycush)+from+its+prey.">Net trophic transfer efficiencies of polychlorinated biphenyl congeners to lake trout (Salvelinus namaycush) from its prey.</a> Environmental Toxicology and Chemistry. 31 (12), 2821-2827 (2012).</li><li>Madenjian, C. P., O'Connor, D. V. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Laboratory+evaluation+of+a+lake+trout+bioenergetics+model.">Laboratory evaluation of a lake trout bioenergetics model.</a> Transactions of the American Fisheries Society. 128 (5), 802-814 (1999).</li><li>Ballschmiter, K., Bacher, R., Mennel, A., Fischer, R., Riehle, U., Swerev, M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+determination+of+chlorinated+biphenyls,+chlorinated+dibenzodioxins,+and+chlorinated+dibenzofurans+by+GC-MS.">The determination of chlorinated biphenyls, chlorinated dibenzodioxins, and chlorinated dibenzofurans by GC-MS.</a> HRC Journal of High Resolution Chromatography. 15 (4), 260-270 (1992).</li><li>Madenjian, C. P., David, S. R., Pothoven, S. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Effects+of+activity+and+energy+budget+balancing+algorithm+on+laboratory+performance+of+a+fish+bioenergetics+model.">Effects of activity and energy budget balancing algorithm on laboratory performance of a fish bioenergetics model.</a> Transactions of the American Fisheries Society. 141 (5), 1328-1337 (2012).</li><li>Lieb, A. J., Bills, D. D., Sinnhuber, R. O. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Accumulation+of+dietary+polychlorinated+biphenyls+(Aroclor+1254)+by+rainbow+trout.">Accumulation of dietary polychlorinated biphenyls (Aroclor 1254) by rainbow trout.</a> Journal of Agricultural and Food Chemistry. 22 (4), 638-642 (1974).</li><li>Niimi, A. J., Oliver, B. 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For de mest nøyaktige estimater av γ må experimenter være i stand til nøyaktig å spore både mengden av mat plassert i hver av tankene og mengden uspist mat i hver av tankene i løpet av eksperimentet. For å oppnå dette, må experimenter være i stand til å fjerne alle de oppspore mat fra tankene og nøyaktig bestemme vekten. I tillegg til nøyaktig sporing av maten faktisk spist av rovfisk, kan nøyaktig estimering av γ også avhenge av tilstrekkelig varighet av forsøket. Gitt at mye sitert laboratoriestudie...

Of all of the factors affecting the rate at which fish accumulate contaminants, the efficiency with which fish retain contaminants from the food that they eat is one of the most important1-3. Risk assessment models have been developed to predict future risks to both people and wildlife eating contaminated fish under various scenarios of environmental contamination, and the reliability of these predictions critically depends on the accuracy of the estimates of the efficiency at which fish retain contaminants from their food4.
The efficiency with which the contaminant in the food ingested by the predator is transported through the gut wall is known as gross trophic transfer efficiency5. A portion of the quantity of the contaminant transported through the gut wall of the predator may eventually be lost through depuration and/or metabolic transformation. The efficiency with which the contaminant in the food ingested by the predator is retained by the predator, including any losses due to elimination and metabolic transformation, is known as net trophic transfer efficiency6.
Gross trophic transfer efficiency of organic contaminants to fish from their prey appears to vary with the contaminant&#8217;s chemical properties, including lipid affiliation as measured by the octanol-water partition coefficient, Kow3,7. According to an empirical relationship developed by Thomann3, gross trophic transfer efficiency is relatively high when log Kow is equal to a value between 5 and 6. Gross trophic transfer efficiency declines exponentially at a rate of 50% per unit of log Kow as log Kow increases from 6 to 10, according to the Thomann3 relationship.
Nevertheless, the gross and net trophic transfer efficiencies of polychlorinated biphenyl (PCB) congeners to fish from their prey do not appear to follow the Thomann3 relationship in most cases. Although the trophic transfer efficiencies of PCB congeners to lake whitefish (Coregonus clupeaformis) from its food followed the relationship proposed by Thomann8, trophic transfer efficiencies of PCB congeners were either just weakly related or not related at all to log Kow for Atlantic salmon (Salmo salar)9, rainbow trout (Oncorhynchus mykiss)10, coho salmon (Oncorhynchus kisutch)11, and northern pike (Esox lucius)11.
The overall goal of this study was to present a laboratory technique for estimating the net trophic transfer efficiencies of PCB congeners to a piscivorous fish from its prey. Lake trout (Salvelinus namaycush) was chosen as the piscivorous fish for our experiment because lake trout are relatively easy to maintain in laboratory tanks. Bloater (Coregonus hoyi) was selected as the prey fish to be fed to the lake trout because bloater is eaten by lake trout in its natural setting12. In addition, we determined whether the net trophic transfer efficiencies for lake trout estimated from our laboratory experiment followed the Thomann3 relationship. We also determined whether the degree of activity by the lake trout had a significant effect on net trophic transfer efficiency (&#947;) of the PCB congeners. Activity by lake trout in the Laurentian Great Lakes is believed to have recently increased because changes in the food webs have caused lake trout to allocate more energy toward searching for food13. Lake trout were forced to exercise in one set of tanks by subjecting these lake trout to relatively high flow rates, whereas the other lake trout were permitted to remain relatively inactive by subjecting them to relatively low flow rates. Finally, the specific details of our laboratory procedure that need to be carefully followed to ensure the highest degree of accuracy in the &#947; estimates and to make the laboratory results applicable to the field are discussed, as well as future directions for research building on our laboratory technique. Net trophic transfer efficiency can be estimated both in the laboratory and in the field, and advantages and disadvantages are associated with both approaches. Accuracy in the estimate of &#947; depends on the accuracy of the estimate of food consumption. The amount of food eaten by fish in the laboratory can be accurately determined when proper protocols are followed, whereas the amount of food eaten by fish in the field is typically estimated via bioenergetics modeling. Use of bioenergetics modeling to derive the amount of food eaten has the potential to introduce a substantial amount of uncertainty into the estimates of food consumption. Fish bioenergetics models have been shown to estimate food consumption with no detectable bias for the case of lake trout14,15, but considerable bias in bioenergetics model estimates of food consumption has been detected for the case of lake whitefish15,16. On the other hand, estimates of net trophic transfer efficiency estimated in the laboratory may not be applicable to the field due to a difference in feeding rates between the laboratory and the field17. Evidence from both the laboratory and the field suggest that feeding rate can influence &#947;14,17.
The methodology used in the present study for estimating &#947; in the laboratory is applicable to situations where the predator fish is fed prey fish, and the amount of prey fish eaten by the predator can be accurately tracked. To accomplish this, the experimenter must weigh all of the food before placement in the tank; and the experimenter must be able to remove all of the uneaten food from the tank, and then weigh the uneaten food. In addition, an adequate suite of mixers and blenders should be available to obtain a sufficient degree of homogenization of the samples of both predator and prey fish. Finally, the gas chromatography &#8211; mass spectrometry instrumentation used to determine the PCB congener concentrations must be capable of detecting and quantifying individual PCB congeners at relatively low concentrations.

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			<td height="21" style="height:21px;width:259px;">Name&#160;</td>
			<td style="width:87px;">Company</td>
			<td style="width:119px;">Catalog Number</td>
			<td style="width:167px;">Comments</td>
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			<td height="21" style="height:21px;width:259px;">2,380-L fiberglass tanks</td>
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			<td style="width:119px;">RT-630-1</td>
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			<td height="34" style="height:34px;width:259px;">Ashland chef knife</td>
			<td style="width:87px;">Chicago Cutlery</td>
			<td style="width:119px;">SKU 1106336</td>
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			<td style="width:119px;">3863586</td>
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			<td height="34" style="height:34px;width:259px;">1.9-L food processor</td>
			<td style="width:87px;">Robot Coupe, Inc.</td>
			<td style="width:119px;">RSI 2Y1&#160;</td>
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			<td style="width:87px;">Arcan Inc.</td>
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			<td style="width:119px;">220-0125</td>
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			<td style="width:87px;">Mettler Toledo</td>
			<td style="width:119px;">Mettler PM 6000&#160;</td>
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			<td style="width:87px;">EMD</td>
			<td style="width:119px;">SX0760E-3</td>
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			<td height="35" style="height:35px;width:259px;">Glass extraction thimbles (45 mm x 130 mm)</td>
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			<td style="width:119px;">LG-7070-114</td>
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			<td height="21" style="height:21px;width:259px;">Teflon boiling chips</td>
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			<td style="width:119px;">919120</td>
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			<td style="width:87px;">Organomation</td>
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			<td style="width:119px;">&#160;LG-6900-104</td>
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			<td height="35" style="height:35px;width:259px;">Hexane</td>
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			<td style="width:119px;">Cat. 300-4</td>
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			<td height="21" style="height:21px;width:259px;">Silica gel</td>
			<td style="width:87px;">BDH</td>
			<td style="width:119px;">Cat. BDH9004-1KG</td>
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			<td style="width:87px;">Lab Line Instruments</td>
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			<td height="35" style="height:35px;width:259px;">Agilent 5973 GC/MS with chemical ionization</td>
			<td style="width:87px;">Agilent</td>
			<td style="width:119px;">5973N</td>
			<td></td>
		</tr>
		<tr height="52">
			<td height="52" style="height:52px;width:259px;">Internal standard solution&#160;</td>
			<td style="width:87px;">Cambridge Isotope Laboratories</td>
			<td style="width:119px;">EC-1410-1.2</td>
			<td></td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:259px;">PCB congener calibration standards</td>
			<td style="width:87px;">Accustandard</td>
			<td style="width:119px;">C-CSQ-SET</td>
			<td></td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:259px;">DB-XLB column (60m x 0.25mm, 0.25 micron)</td>
			<td style="width:87px;">Agilent/ J&#38;W</td>
			<td style="width:119px;">122-1262</td>
			<td></td>
		</tr>
	</tbody>
</table>

laboratory estimation of net trophic transfer efficiencies of pcb congeners to lake trout (salvelinus namaycush) from its prey

En teknikk for laboratorium estimering av netto trofisk overføringseffektivitet (γ) av polyklorerte bifenyler (PCB) enere til piscivorous fisk fra deres byttedyr er beskrevet her. I løpet av en 135-dagers laboratorieeksperiment, matet vi bloater (Coregonus hoyi) som hadde blitt fanget i Lake Michigan til storørret (Salvelinus namaycush) holdt i åtte laboratorietanker. Bloater er et naturlig byttedyr for storørret. I fire av tankene, er en relativt høy strømningshastighet brukes til å sikre relativt høy aktivitet ved sjø-ørret, mens en lav strømningshastighet ble benyttet i de fire andre tanker, slik at for høy sjø-ørret aktivitet. På en tank-til-tank basis, ble mengden av mat som spises av sjø-ørret på hver dag av forsøket registreres. Hver innsjø ørret ble veid ved starten og slutten av forsøket. Fire til ni sjø-ørret fra hver av de åtte tankene ble avlivet ved starten av forsøket, og alle 10 sjø-ørret gjenværende i hver av tankene var euthansert ved slutten av forsøket. Vi bestemte konsentrasjoner av 75 PCB-forbindelsene i sjøen ørret ved starten av forsøket, i sjøen ørret ved slutten av forsøket, og i bloaters matet til sjø-ørret i løpet av eksperimentet. Basert på disse målingene ble γ beregnet for hver av 75 PCB-forbindelsene i hver av de åtte beholdere. Middel γ ble beregnet for hver av de 75 PCB-forbindelsene for både aktiv og inaktiv sjø-ørret. På grunn av at forsøket ble replikert i åtte beholdere, standard feil om betyr γ kunne estimeres. Resultatene fra denne type forsøk er nyttige i risikovurderingsmodeller for å forutsi fremtidig risiko for mennesker og dyreliv spiser forurenset fisk under ulike scenarier for miljøforurensning.

Lake ørret viste en betydelig mengde vekst i løpet av eksperimentet, som den innledende sjø-ørret betyr vektene varierte 694-907 g, mens den endelige sjø-ørret betyr vektene varierte fra 853 til 1566 g (Tabell 1). Den gjennomsnittlige mengden mat konsumert av en innsjø ørret i løpet av den 135-dagers eksperiment varierte fra 641 til 2649 g. Mener PCB kongener konsentrasjoner i sjøen ørret økte i løpet av forsøket, som gjennomsnitt PCB kongener konsentrasjoner varierte 0,01 til 7,14 ng / g ...

Watch this Scientific Journal Video about Laboratory Estimation of Net Trophic Transfer Efficiencies of PCB Congeners to Lake Trout Salvelinus namaycush from Its Prey at JoVE.com

Laboratory Estimation of Net Trophic Transfer Efficiencies of PCB Congeners to Lake Trout Salvelinus namaycush from Its Prey

En teknikk for laboratorium estimering av netto trofisk overføring effektiviteten av polyklorerte bifenyler (PCB) enere til piscivorous fisk fra deres byttedyr er presentert. For å maksimere anvendelsen av laboratorieresultatene til feltet, bør piscivorous fisken mates byttefisk som vanligvis spises i felten.

Laboratory Estimering av Net trofiske overføringer effektiviteten av PCB-forbindelsene til Lake Trout (<em&gt; Salvelinus namaycush</em&gt;) Fra sitt bytte

A technique for laboratory estimation of net trophic transfer efficiency (&#947;) of polychlorinated biphenyl (PCB) congeners to piscivorous fish from ...

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Environment

Laboratory Estimation of Net Trophic Transfer Efficiencies of PCB Congeners to Lake Trout (Salvelinus namaycush) from Its Prey

Laboratory-determined Phosphorus Flux from Lake Sediments as a Measure of Internal Phosphorus Loading

Laboratory bestemt Fosfor Flux fra innsjøsedimentene som et mål på intern Fosfor Loading

Eutrophication is a water quality issue in lakes worldwide, and there is a critical need to identify and control nutrient sources. Internal phosphorus (P) ...

A Fish-feeding Laboratory Bioassay to Assess the Antipredatory Activity of Secondary Metabolites from the Tissues of Marine Organisms

A Fish-fôring Laboratory Bioassay å Vurdere Antipredatory aktivitet av sekundære metabolitter fra vev av marine organismer

Marine chemical ecology is a young discipline, having emerged from the collaboration of natural products chemists and marine ecologists in the 1980s with ...

Automated Gel Size Selection to Improve the Quality of Next-generation Sequencing Libraries Prepared from Environmental Water Samples

Automatisert Gel Størrelse Selection å forbedre kvaliteten på Neste-generasjons Sekvense Biblioteker Forberedt fra miljø vannprøver

Next-generation sequencing of environmental samples can be challenging because of the variable DNA quantity and quality in these samples. High quality DNA ...

Removal of Trace Elements by Cupric Oxide Nanoparticles from Uranium In Situ Recovery Bleed Water and Its Effect on Cell Viability

Removal of Trace Elements by Cupric Oxide Nanoparticles from Uranium In Situ Recovery Bleed Water and Its Effect on Cell Viability

Fjerning av Trace Elements av Cupric Oxide Nanopartikler fra Uran<em&gt; In Situ</em&gt; Recovery Bleed Vann og dens effekt på Cell Livskraftig

In situ recovery (ISR) is the predominant method of uranium extraction in the United States. During ISR, uranium is leached from an ore body and extracted ...

Laboratory Simulation of an Iron(II)-rich Precambrian Marine Upwelling System to Explore the Growth of Photosynthetic Bacteria

Laboratory Simulation of an IronII-rich Precambrian Marine Upwelling System to Explore the Growth of Photosynthetic Bacteria

Laboratory Simulering av en Iron (II) rik prekambrium Marine Oppstrømning System til Utforsk Vekst av fotosyntetiske bakterier

A conventional concept for the deposition of some Precambrian Banded Iron Formations (BIF) proceeds on the assumption that ferrous iron [Fe(II)] upwelling ...

Development of Metarhizium anisopliae as a Mycoinsecticide: From Isolation to Field Performance

Development of Metarhizium anisopliae as a Mycoinsecticide: From Isolation to Field Performance

Utvikling av<em&gt; Metarhizium anisopliae</em&gt; Som Mycoinsecticide: Fra Isolasjon til Field Performance

A major concern when developing commercial mycoinsecticides is the kill speed compared to that of chemical insecticides. Therefore, isolation and ...

Procedures of Laboratory Fumigation for Pest Control with Nitric Oxide Gas

Prosedyrer for laboratoriet utgassing til skadedyrbekjempelse med nitrogenoksid gass

Nitric oxide (NO) is a newly discovered fumigant for postharvest pest control. This paper provides detailed protocols for conducting NO fumigation on ...

Adherence of Bacteria to Plant Surfaces Measured in the Laboratory

Overholdelse av bakterier å plante overflater måles i laboratoriet

This manuscript describes a method to measure bacterial binding to axenic plant surfaces in the light microscope and through the use of viable cell ...

Ecosystem Fabrication (EcoFAB) Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions

Ecosystem Fabrication EcoFAB Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions

Økosystem fabrikasjon (EcoFAB) protokoller for bygging av laboratoriet økosystemer designet anlegg-mikrobe interaksjoner

Beneficial plant-microbe interactions offer a sustainable biological solution with the potential to boost low-input food and bioenergy production. A ...

Laboratory and Field Protocol for Estimating Sheet Erosion Rates from Dendrogeomorphology

Laboratory og felt protokollen for beregning ark erosjon priser fra Dendrogeomorphology

Sheet erosion is among the crucial drivers of soil degradation. Erosion is controlled by environmental factors and human activities, which often lead to ...