Archive for June, 2010

Aquatic Insect Identifications

Monday, June 28th, 2010

Identification of macroinvertebrate samples from Sublette County, WY is progressing at faster pace with the addition of Esmeralda to our team.  She is a meticulous sorter and has a sorting efficiency of 97-100%!  This is impressive to me because, some of the other companies I have worked for have the sorters strive for 90%.  The idea is that if sorters remove 90% or more on the first sort, that the sample passes the Quality Assurance Standards of most bioassessment programs BUT that if they exceed it “too much” they are spending too much time on a sample.  Since laboratory work is usually conducted at a fixed price (per sample, regardless of how long it takes), one way to increase the profit margin is to ensure that employees spend as little time on each sample as possible. I wonder, if it is truely more cost effective to have the sorters aim a little lower.

For Example, if a sorting technician speeds through a sample, knowingly missing a few specimens, aiming for 90% efficiency, actually only sorts 70% of the insects. The sample would fail the QA/QC check and need to be re-sorted.  If the rechecked sample is sorted t0 88%, the entire processed portion needs to be sorted… again… Personally, I don’t think this would work well in my lab.  I think that it is more cost effective to take 20% longer to aim 10% higher (aim for 100%), than it is to retrieve the sample from storage, resort it, amending the data later–even if you only have to do that to a small portion of the samples.  But then we are a small capacity laboratory and it feels like our infrastructure is better suited for minimizing re-sorts.  I think it is a fairly valid assumption that the sample that has been re-sorted to 98% efficiency is just as good as the sample that was sorted to 98% efficiency the first time, so it is really about how the labs handle logistics–not so much about data quality. So, Esmeralda, keep up the highly efficient sorting–it is a good fit here!

I did just realized that some readers may not know about the two standard types of Quality Assurance measures applied to benthic macroinvertebrate sample processing: Sorting efficiency, and subsampling consistency.  We just discussed sorting efficiency (above). It is the portion of the total number of specimens found relative to the actual number in the sample. To calculate this number, one person sorts the sample and removes all the specimens from the sample. Later, another investigator examines the sample and removes all the specimens they find.  If the first person found 90 critters, and the second found 10, the first sorter’s efficiency would be 90%.

Sorting efficiency is a measure of the completeness of the sorting effort in the laboratory’s staff and may indicate the need for corrective action, whereas “subsampling consistency” describes some inherent characteristic of the of the samples composition–the clumpiness. Most bioassessment samples are not completely sorted–they are usually subsampled. So, if 25% of a sample was sorted to reach the SOP’s target number of organisms, (100, 200, 300, 500, or 1,000) then another equal portion of the sample (25%) would be analyzed in the laboratory. Both the taxonomic composition and total number of organisms are issues for comparison. Ideally the composition of the two portions taken from the same sample would be very very similar. However, in some instances specimens remain clumped together and one subsample is quite different from another portion of the sample. There is really nothing that can be done about this within the confines of study design.  If you add the two samples together, the new sample represents twice as much effort as the other samples in the study and would violate several assumptions in the analysis. If you keep them separate they violate other assumptions. Thus the number serves as a warning sign about the amount of variation with in a sample… Subsampling consistency involves as much work as a new sample, so it costs the same as an additional sample. Thus, most clients do not elect to perform this analysis on their benthic samples.  If a state agency routinely sends out 300 samples in a year, they would need to pay for 30 additional (~$9,000) samples to have subsampling consistency checks on 10% of their samples.  I think I can understand their desire to spend those funds sampling additional samples rather than describing an uncontrollable aspect of  sample composition. The flip side is if they assume the samples are 100% uniform and representative, some poor decisions can be made.

More on the effect of subsampling efficiency latter. Meanwhile, here is a thought question: Why do you think sorting efficiency matters?

~Jefferson River Montana~

Friday, June 25th, 2010

The Jefferson River Flooded last weekend. All the hay fields in the area were flooded and roads that have not been submerged in recent history became gentle rivulets. The High water is good for the Jefferson River because it has had many years of below average flows–and fine sediments have built up among the interstitial spaces were many invertebrates that are important fish forage live.

When Snorkeling in recent years, I have found that if you pick up a cobble, there is beneath it only sand. Typically, you might expect to find more cobbles under cobbles. Among the sand grains are the burrows of several sediment dwelling invertebrates (e.g., Hexagenia and Ephoron sp.). According to locals, the river once supported impressive hatches of large stoneflies (Hesperoperla pacifica, Pteronarcys sp. etc).

When sediment fills in the the area under the stones, much of the habitat used buy large stone flies is lost because the interstitial spaces are simply too small for them to pass through. This results in smaller populations (of large invertebrates), and ultimately smaller hatches. It may also reduce the forage available for fish. For example, it appears that sedimentation of the Jefferson River may have caused Burrowing dragonflies (Gomphidae) to replace many of the large predatory stoneflies typically expected. We sampled the Jefferson River several years ago and found about 2-3 gomphid dragonflies per square foot and about 0.3 large stoneflies in the same area–the dragonflies were nearly 10x times as abundant as the stoneflies.  We are hopeful  that high river levels will scour sand from interstitial spaces and improve survival of stoneflies. This could result in an improvement in fishing a few years down the road…

Aside from benefiting river ecology, another effect of the flood is that pools and back waters that have not been flooded for years have now been nicely inundated for a week or more. Mosquito eggs can remain dormant for several years–until they become wet.  We found hundreds of thousands of mature mosquito larvae and pupae among the grassy ditches and fields last weekend. There were so many larvae, that in just a few minutes we observed hundreds of larvae washing across the road in shallow riffles (picture below).  By this weekend or early next week the Jefferson Valley will likely be swarmed by endless squadrons mosquitoes… and it has been such a nice spring.  If you can tolerate the bites and buzzing it might be a nice weekend to try mosquito-mimic flies… and if you have a friend who owns a hay field… maybe see if you can get permission to fish it!

mosquitoes float across the road

~Holston River Tennessee~

Thursday, June 24th, 2010

The Zone of periodically inundated waters is called the “varial zone” and the community structure can deviate dramatically from the structure of permanently inundated river bottom.

RiverContinuum.org

We are gearing up for our joint venture with the Academy of Natural Sciences to sample the Holston River near Kingsport Tennessee. I last surveyed this river when I managed the Invertebrate Zoology Research section of the Academy’s Patrick Center for Environmental Research in 1997.  The Academy will be collecting water chemistry, algae, fish, qualitative non-insect macroinvertebrates, and quantitative insects (that’s me!) From July 10-July 20 2010.

The project is difficult because the flow of the river fluctuates with hydro-power generation. High water can present safety challenges, but it can also produce sampling challenges. For example, we don’t want to sample part of the river that was bone-dry two hours earlier… it would definitely cause confounding results when the data are compared to locations that were sampled in perennial flowing zones.  The Zone of periodically inundated waters is called the “varial zone” and the community structure can deviate dramatically from the structure of permanently inundated river bottom.  Fortunately, on the Holston we can tell if the rocks were recently exposed to the air for long time periods because stones become crusted with algae or sediment.

Spending a little time identifying the varial zone boudary can really save you from heartache latter, when you try to explain why the study’s results are confounded by sampling issues.  To help avoid these problems, we will spend a day visiting the sites to grab flow measures and identify the amount of lateral/vertical changes in river height (depth).  Also, local news papers usually publish river gauge stage readings and the USGS web page can often provide real-time river height information.  One thing to remember is that these readings are usually reported from dams or bridges, and it may take several hours from from the time a flow spike is recorded and the time it reaches your sample location. If you spend sometime before sampling you can get a feel for time of lowest water at each location.

The Sampling device we will use is the Portable Invertebrate Box Sampler (PIBS)– for those in the know, it is like a rectangular, enclosed Surber Sampler with a foam-sealing base.  It can be used in water depths from 10cm to ~35-40 cm without modification. Therefore, in rivers like the Holston, it is important to try to sample at the period of lowest water so you are sure to collect from the perennial zone… Remember, if the water-level is 50 cm higher than base flow, it will be too deep to reach the perennial zone with the sampler… The Surber would require even a shallower (<30cm) high flow to be effective. Hess samplers are highly variable in their construction and can be modified to work in deeper water, but remember the limiting factor is the length of your arms… if you can’t reach the bottom of the sampler to scrub the cobbles, you cant collect the sample.

I am personally excited by this trip because the downstream site, is one of the most diverse benthic assemblages… it is absolutely lovely!

~New Fork River~

Thursday, June 24th, 2010
The Mona Lisa

Photo: B. Marshall

We have been working most of the winter on samples from the New Fork River and the Upper Green River in Sublette County Wyoming. It is fun to get back into the grove of identifying samples.   We just hired a new Technician Esmeralda (who’s bio is not yet posted on the web page) to help make the report deadline. Esmeralda is incredibly efficient and a welcome relief to laboratory staff.  Sorting is now proceeding at a much faster pace.

One of the interesting specimens we’ve found is a tusked Paraleptophlebia nymph.  There are two western species of Paraleptophlebia that have tusks that are believed to assist with burrowing (P. bicornuta and P. Packi). The outer margin of the mandible is expanded to form the tusks and the head is more directed forward (prognathous) than in other species of Paraleptophlebia making the nymphs appear different and more predatory.

Edmunds and McCafterty (1996) compared the behaviors of burrowing mayflies and reported, “Paraleptophlebia packi forms burrows in silt, whereas P. bicornuta is an interstitial dweller.”  It would be interesting to differentiate these species because the impacts we have been discussing in the report are related localized sedimentation related to gas well development and other land use activities. Changes in the relative abundance of these species might result from changes in the amount of sediment entrained in the river. Unfortunately it is very difficult to separate nymphs of these species with “nice” specimens and ours are not in ideal condition. Furthermore, it is not clear when the tusks become apparent; many of our younger Paraleptophlebia nymphs may be P. packi or P. bicornuta that have not yet developed the prominent tusks which differentiate them from other species. Thus, even if we were to differentiate the species with mature speciemens, ontogenic  morphological changes within the species might cause spurious results when most of the nymphs are immature.

Thought Question: How else might ontogeny affect biological assessments of streams and rivers?