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# DMA Operating Protocol | ||
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For a typical daily sample run | ||
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### Cleaning Procedure | ||
To clean used quartz boats: | ||
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1. Gently scrape ash out of quartz boats with spatula and/or kimwipes. | ||
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2. Rinse quartz boats in acetone. Perform this step in the fume hood to prevent inhalation | ||
of harmful acetone vapors. | ||
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3. Rinse quartz boats in deionized water and place on rack to air dry. | ||
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4. Place quartz boats in DMA turntable. | ||
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5. Open new “sample” file under the “measurements” tab. | ||
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6. Enter 1.0 gram weight for each empty quartz boat to clean. | ||
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7. Under the “Methods” tab, select “cleaning procedure”. | ||
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8. Under the “Calibration” tab select current calibration file. | ||
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9. Return to sample and save sample file as “trash.” | ||
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10. Start DMA and the cleaning procedure begins. | ||
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11. Once the procedure is complete, determine if any sample boats had high levels of Hg | ||
residue (>0.005 mg/kg.) These boats may need to be burned again. | ||
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### Starting Up the DMA | ||
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To prepare the DMA for sample runs each morning, it is necessary to remove residual Hg within | ||
the machine and check the accuracy of the calibration curve. | ||
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1. Turn DMA-80 machine on using power button | ||
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2. Open oxygen tank and adjust pressure to just below 60 PSI | ||
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3. Login on the terminal by selecting “administrator” and entering the password “123456” | ||
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4. Wait for the machine to warm up (about 15 minutes) and when it is ready the start | ||
button will become functional | ||
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5. Under the “Measurements” tab, select the “sample” tab and select the blank sheet to | ||
start a new file. Save file as “trash” | ||
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6. Run two “ghost samples” i.e. no boats in positions 1 and 2 on the turntable to vaporize | ||
any mercury that may remain in the system. Select “clean procedure” in the “Methods” | ||
tab. | ||
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7. Under the “Measurements” tab, select the “sample” tab and select the blank sheet to | ||
start a new file. Select the add line button for each sample. Save file as trash. | ||
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8. Run two samples of powdered standards dorm and dolt to determine machine is still | ||
accurately calibrated. Select “organic fish” in the methods tab and current calibration | ||
curve in the calibration tab. Dorm and dolt mg/kg of Hg should fall within the given | ||
ranges. | ||
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### Running Samples | ||
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When running bird samples in the machine, each run must be accompanied by blanks and | ||
standard reference materials to make sure the machine is performing the analysis accurately. | ||
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1. Under the “Measurements” tab, select “Sample,” and select the new file button to | ||
create a new sample file. Select the add line button for each sample. | ||
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2. Under the “Methods” tab, select organic fish method | ||
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3. Under the “Calibration” tab, select desired calibration curve file | ||
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4. Return to “Measurements” tab and save sample file with desired file name (e.g. | ||
mm_dd_yyyy_feathers_LG) | ||
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5. Place a clean and empty sample boat in turntable position 1 as a blank. Enter 1.0 | ||
gram for the weight. | ||
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6. Weigh around 0.025 grams of dorm, dolt, and tort standards and place boats in | ||
turntable positions 2, 3, and 4. Enter actual weight and sample names in sample | ||
sheet. | ||
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7. Weigh albumen, blood, or feather samples one at a time using analytical scale and | ||
place boats in the correct turntable positions. Record data from samples on data | ||
sheet. | ||
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8. Enter sample ID and weight in grams in the sample table. | ||
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9. Save sample file again. After all samples have been measured and placed in the | ||
turntable, hit the green start button to begin the analysis. | ||
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10. Once the run begins, make sure the method and calibration selected are still | ||
selected (*sometimes the machine switches the calibration file on its own, we don’t | ||
want that to happen) | ||
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11. Once sample run is complete, save the measurement file, and record the mercury | ||
concentration mg/kg on the datasheet. | ||
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12. Place datasheet in binder |
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# Feather Sampling for Mercury | ||
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### Background and Rationale: | ||
Mercury is a heavy metal that has no known biological function in any organism. | ||
It is therefore not a trace element, and a contaminant at any level. Its detrimental | ||
effects on wildlife at high doses have been known for some time (severe neuronal | ||
degeneration, powerful developmental effects) but the effects at low levels are only just | ||
being discovered, particularly in wild populations of fish and birds (reproductive failure, | ||
endocrine disruption, loss of appetite, increased susceptibility to disease, and others). | ||
Under anaerobic conditions prevalent in many wetlands, elemental mercury (the | ||
stuff in thermometers) may be converted to methylmercury as a byproduct of the | ||
metabolism of sulfur-reducing bacteria. Methylmercury is at least ten times more toxic | ||
than elemental mercury, in part because it can cross the blood-brain barrier, and in part | ||
because it is excreted very slowly. Because of the latter property, it also bioaccumulates | ||
very efficiently in wetland food webs. | ||
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In most terrestrial and lake systems, mercury eventually accumulates in | ||
sediments where it is largely unavailable to biota. But in shallow wetlands that wet and | ||
dry regularly, mercury in sediments is regularly re-exposed and recycled. So wetlands | ||
like the Everglades are extremely good at keeping mercury available, and keeping it in | ||
its most toxic form. | ||
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During the late 1980’s and 1990’s, Everglades biota were extremely | ||
contaminated with mercury, with some of the highest values measured in vertebrates | ||
recorded – this was true for predatory fishes, mammals and wading birds. The | ||
contamination from mercury resulted in direct mortality of some Florida Panthers, | ||
endocrine disruption in birds, and probably reduced fecundity and survival in birds and | ||
fishes. Human consumption advisories were issued for Largemouth Bass and other | ||
predatory freshwater fishes. | ||
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The mercury was coming largely from municipal waste incinerators in the urban | ||
areas of Miami and Ft. Lauderdale. Beginning in the early 1990’s, federal legislation | ||
mandated that mercury be taken out of household batteries, a major source of mercury | ||
in municipal waste. Florida (and later federal) legislation also mandated the installation | ||
of scrubbers on municipal waste stacks, further reducing emissions of mercury aerosols | ||
and particulates. | ||
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After about a 7-year lag time, mercury concentrations in Everglades biota began | ||
dropping precipitously – a 75% reduction in two years, for example. The existence of the | ||
mercury problem in wildlife, and the massive reduction in contamination, were both the | ||
result of a long-term mercury sampling program in the Everglades for sport fishes and | ||
for wading birds. | ||
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Although mercury may have declined for good, there remain good reasons for | ||
continuing to monitor for mercury contamination. First, it’s not clear that mercury will | ||
remain low – in years following droughts, for example, we may expect to see spikes of | ||
mercury that result from re-liberating mercury tied up in sediments. These spikes could | ||
turn out to be a natural experiment that allows further understanding of the effect of | ||
mercury on nest success. Second, other mercury sources could emerge over time – | ||
some of these might be through atmospheric deposition, or other currently unknown | ||
local sources. Keep in mind that none of the mercury contamination or its decline in the | ||
1980’s and 1990’s would have been discovered without fish and bird monitoring. | ||
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### Sampling – tissue, age group and species | ||
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Nearly all of the mercury in fish is in the methylated form, and consequently the | ||
same is true in birds. Birds are able to excrete methylated mercury primarily through | ||
feathers as they grow, largely because methylmercury has a very strong affinity for | ||
keratinized tissue. So feathers serve as an accurate record of the amount of mercury | ||
circulating in the birds body at the time that the feathers were grown. The | ||
concentrations of methylmercury in feathers are quite large relative to the amounts in | ||
other tissues, and so feathers give a strong and definite signal if mercury is present. | ||
Feathers from adult birds have two problems – we don’t usually know when they | ||
were grown, and we don’t know where they were grown. Thus they could represent | ||
mercury contamination acquired from outside the Everglades. Young birds are an | ||
excellent indicator, however, if feathers are collected while they are growing. We know | ||
from research that not much mercury gets into young from the egg resources, and we | ||
also know that all of the food the chick gets comes from an easily defined area | ||
surrounding the colony. Chicks are also growing feathers at a rapid rate, and are getting | ||
lots more food per body weight than are adults – so they are excellent bioaccumulators, | ||
and excellent bioindicators of mercury in prey items in the surrounding marsh. | ||
As an aside, the chicks are growing so many feathers during the fast growth | ||
period, they are in effect protected from the effects of methylmercury – nearly all gets | ||
excreted into the feathers. It’s when they stop growing feathers and fledge that the | ||
nasty effects of mercury probably come into play. | ||
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We sample feathers from Great Egret chicks – these animals feed almost | ||
exclusively on fish, they are relatively high in the trophic web, they nest reliably from | ||
year to year, and typically nest throughout the study area. So we can get good | ||
geographic representation that is reliable from year to year. | ||
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Typically, there are large differences in contamination between colonies in | ||
different parts of the Everglades as a result of “hotspots” of mercury contamination. | ||
These differences are probably due to a complicated mix of water and soil chemistry | ||
factors that favor or disfavor the bacteria that methylate (or demethylate) mercury. | ||
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### Sampling protocol | ||
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#### Safety: | ||
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Make absolutely sure everyone has eye protection and wears it during | ||
the capture attempt. Those with dime store sunglasses should not consider them | ||
adequate protection. They also tend to be taken off in cloudy or closed canopy | ||
environments, so make everyone who doesn’t were prescription glasses to carry and | ||
use safety goggles or something comparable. Take care too if prescription glasses are | ||
small. The bird’s bill can slip under or around them and still reach the eye. | ||
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#### Where to sample: | ||
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Aim to sample chicks from 5 – 10 colonies. In the past, we | ||
have usually sampled from Alley North, JW1 (not recently active), L-67 (a.k.a. Horus), | ||
Vacation, Hidden, Tamiami West, Mud Canal, and 3B Mud Canal. Typically, one or more | ||
of these colonies will not be active or accessible in any year, so we may substitute | ||
others. We are now collecting in cooperation with the SFWMD. Check with Ms. Shane | ||
Atkins ( [email protected] ) before the nesting season begins in earnest. | ||
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#### When to sample: | ||
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When chicks are large enough to walk and young enough they | ||
do not walk or fly fast enough to escape you. The older, the better. To gauge this, you | ||
need to know the approximate date of laying eggs or hatching chicks – this should be | ||
done either from aerial surveys or (preferably) from visits on the ground. | ||
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#### What to collect: | ||
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Feathers from the scapular region – middle of the back in | ||
between the shoulders. Feathers should be fairly well developed to obtain enough | ||
material – newly erupting ones are not appropriate. If the birds you are sampling are | ||
mostly down, you are way too early. The birds need to be able to stand up on their own, | ||
and probably run from the nest. Feathers should be pulled individually (not in bunches) | ||
with a quick, firm yank in a direction parallel to the angle of insertion in the skin. These | ||
feathers may be well connected to the blood supply, being growing feathers. If a feather | ||
shaft is broken off, it could allow heavy bleeding – make sure the entire feather base | ||
comes out. If it bleeds heavily, try to remove all of the shaft, and damp bleeding with | ||
cotton until it clots. Collect at least five feathers 2 – 3 inches long, and ten if you can get | ||
them. | ||
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Be sure to measure the bill length (culmen, tip of bill to beginning of skin on | ||
dorsal surface of bill) for each bird – this gives us a way to correct each sample for age. | ||
We have also been taking weight information, but this may be optional. Check with | ||
SFWMD. | ||
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Very often, the birds will regurgitate their most recent meal. This is unavoidable, | ||
and since you cannot stuff it back in, you may as well collect it. Take extra ziplocs, and | ||
label the sample by date, colony, and culmen of the bird that threw it up. Keep boluses | ||
from individuals separate. Place in a cooler on the boat, and in the freezer AS SOON as | ||
you get back home. | ||
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What to do with the bird after you’re done: Release it back into the nest or as | ||
close to the nest as is possible. Be sure to get the rest of the crew out of the nest area in | ||
the future direction of travel. Sometimes the juv seems frozen after its release and may | ||
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be experiencing some level of stress or injury. In that case, walk slowly up to it and | ||
encourage it to move a foot or two. It’s wise to carry a small first aid kit to treat any | ||
injuries, bird or biologist. | ||
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#### Marking and storage: | ||
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Each feather sample should be placed in a marked paper | ||
envelope or ziplock bag. Paper envelopes are preferable because pulpy tissue attached | ||
to the base of the feather will rot and not dry in plastic. However, plastic bags may be | ||
used in the field in wet conditions. If plastic is used, samples MUST be transferred to | ||
paper as soon as you return for the day. Mark each envelope sample individually – never | ||
mix birds. Note the colony, date, culmen, number of chicks in the nest (if available) and | ||
the hatch order of the chick in the nest if known. | ||
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#### Sample size in each colony: | ||
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We try to get between 10 and 20 individual birds in each colony. We only sample one chick from each nest, and only the eldest (largest). | ||
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How to catch chicks – Chicks may very well be large enough to leave the nest by | ||
walking or climbing at the age you are supposed to be sampling. Often the trick is to | ||
approach the nest from two or more sides simultaneously. Mirror poles help – try to | ||
hook the bird’s leg, or apply pressure on the head or neck (without hurting the bird) | ||
enough to slow the bird down to the point that it can be caught. Speed and agility are | ||
important here, so do those leg stretches and hyperventilating before you get into the | ||
colony. Note that at this stage if the bird leaves its nest it can generally get back in on its | ||
own. So if you chase but cannot catch a bird, don’t fret about its fate too much. |
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# Feather Mercury Monitoring | ||
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Measurements for Hg levels in individual feathers. | ||
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### Field Collection Methods | ||
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Field collection methods are described in Feather_Mercury_Collection. | ||
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### Hg Analyzer Methods | ||
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A quick guide to protocol is listed in DMA_Protocol. |
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