Archive for the ‘Projects’ Category

Yellowstone River Oil Spill- Redeux

Tuesday, August 23rd, 2011

Well, you may have noticed that I have not said anything about the Yellowstone River Oil Spill since our original entry. Yet, in truth, we have been busily working on the project in-house.  The experience has not been all-together positive; quite the contrary. This entry deals with how the public loses because of bureaucracy; bureaucracy of the corporate breed, not the  governmental red tape I’d expected.

After the oil spill, we contacted Montana Department of Environmental Quality (MT DEQ) for information, they put us in contact with Montana Fish Wildlife and Parks, who deferred us to ExxonMoble’s contact, who put us in touch with a consultant. We discussed my qualifications and my previous work and he reckoned they could use me and my team for the aquatic insect assessments to describe the impact and the recovery of the Yellowstone ecosystem. He sent me an email about once a week to say, they were still trying to bring us on board. After several weeks, he said I better get an OSHA hazardous materials certification and that there was no way around the requirement if I want to work on the Yellowstone River. Several hundred dollars and 3 working-days later (per trainee), we completed the certification.  I informed the contact that we had completed OSHA training as required and didn’t hear back from him for over a week. He said, sorry, “Sorry don’t think its going to work out.” I wrote him a scathing letter; which he apparently passes along to ARCADIS (Exxon’s Primary firm for everything), the next thing I know, I received an 158-page listing of ExxonMoble’s contracting requirements and several 6-9 page contract specifics and insurance requirements.   Again, these were corporate regulations, not governmental regulations.  I had my insurance agent looking into the extra coverages required and it was apparent that it was going to be very costly to bring our $2-million insurance coverage up to the “required” $9-million; just to collect insects by the riverside.

We were working on finalizing their insurance needs when I recieved the following note (today).

“Brett,
It looks like the clock has run out. We have had to mobilize a small field effort to obtain representative macroinvertebrate samples from the spill area. We needed to get out there before fall influenced the life stages we are sampling. Apologies to you if I was in any way misleading regarding your potential role, but we simply did not comprehend the bureaucratic log jams we ran into. Best of luck in the future.”

Ok. So, I am a little embarrassed by my trusting nature and the way I let the corporate dudes string me along.  And, I have always been critical of critics, even when I am the critic.  It is easy to criticize a process or organization, but unless you offer a viable alternative, it amounts to nothing but whining.  My way of dealing with this is to turn it in to something positive.

I reckon that, in preparation for this project it has cost me time, materials, and training fees, totaling nearly $7,300. Interesting that for just another 3o hours of my staff’s time, vehicle costs, and motel lodging, we can collect the samples in a scientifically relevant way.  Therefore, I am proud to announce that we are initiating the Yellowstone Biological Assessment Project, independently, as a community service. There will be laboratory time as well, but hey, that’s what winter nights are for, right…. (?)

If we do not ante up, and get this done right, there will be lots of paper pushed, but the world will be no closer to understanding the impacts of Exxon’s Oil spill on the Yellowstone River ecosystem. Our survey will not be able to cover everything, but it will provide more information than either the state, or Exxon will gather.

We will be sampling this week.   I’ll keep you posted. Full-speed ahead!

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Biological Monitoring Covariates

Thursday, August 5th, 2010

When monitoring environmental impacts of anthropogenic activities, it is useful to collect ancillary data to use as covariates. These variables can help account for natural variation in the communities studies, which helps prevent their confounding of observations. In our work with benthic macroinvertebrate assemblages, we always collect flow measures for this purpose (near-substrate flow measures can account for much of the variation in simple benthic communities (e.g., Hart & Finelli 1999). With a sufficiently rigorous sampling design, the effects of flow on the community can be “teased” out of the analysis, so that the effects of anthropogenic stressors on benthic communities changes can be more accurately assessed–assuming, of course, that flow is not part of the anthropogenic impact in the study area.

Moss, macrophytes, and filamentous algae can also alter the abundance of certain types of macroinvertebrates. Moss, is not palatable to most macroinvertebrates because of the presence of protective chemicals. However, it does offer refuge from the sheer-forces of fast water. It also traps detritus (food), and can increase the amount of surface area available for colonization. Thus the presence of moss can have a strong influence on the structure of macroinvertebrate assembleges sampled in an assessment. When we want to account for this variation, we have found that the simplest (and effective) way, is to take a known amount of alcohol from the preserved samples and rank their Greenness. The Rank can be a very useful covariate when the data are analyzed. Other important covariates usually include a particle index, velocity, and depth.

The assumption is that the “Greenness” of the sample’s preservative is proportional to the amount of material soaking in alcohol for a given amount of time.  Thus, more greenness indicates there is more living plant material collected in the sample. Samples of similar greenness were probably influenced by living plants similarly, whereas the community composition of a very pale sample was probably influenced less by plant material than a sample with deep green preservative.

There are other nuances as well. For example, periphyton may cause a different kind of green tint to preservative than moss does–and it is likely to have a different influence on the benthic assemblage. Fortunately, for our purposes, moss seems to have much stronger effect on the sample’s color than periphyton. Also, you need to ensure that all samples are preserved with the same type and strength of preservative (95% ethanol, or 90% Isopropanol, or 90% denatured ethanol, not some of all three). Samples preserved in formalin would need to be transferred to alcohol before analysis–and even then should not be compared with samples preserved only with ethanol because of formalin’s ability to “fix” pigments.

Holston River

Thursday, July 22nd, 2010

Time for a sort post; please forgive the mushiness I’m short of technical material. I Just got back from my Holston River Survey with the Academy of Natural Sciences.  It was great to see the Holston River again; the invertebrates are especially diverse and familiar–just like old friends. Speaking of old friends, the rest of the Academy crew was also just like old friends… because most of them actually were old friends. It was funny how after 13 years,  most of us fell into our old roles… me: the loose cannon, Paul O: the jokester, Roger: the peace-maker, Richard: The Ivory tower, Frank: the phantom (where’s Frank?); Paul K: the mad scientist (I imagine the first maid to enter Paul K’s room wanted to call the police.) Yet we were all different; three of us had survived life-threatening situations and we were more mellow for it.

There were some new faces (Silvan (Sylvan?), Michelle and Dave)… and I am sure they will forge their own Academy history. They were all intelligent, fun and  hard working; i look forward to seeing them at the Texas Survey this October.  This was my fist survey with Dr. R. William Bouchard Jr., but i have known him for quite sometime.  Will was an intern at the academy when he helped me with midges–now he has a Ph.D. in midges and is an amazing field biologist–just like his dad. I am sure Ray Sr. is proud of the fine young man that will has grown into (quit blushing Will)… enough of the sappy stuff: great fun working with y’all.

Sure, I loved seeing the aquatic insects and other macroinvertebrates of Tennessee, but it was the people that made the trip especially special.

We’ll add pictures in later posts (right Roger?).

Wyoming Educational Benthic Macroinvertebrate Project

Thursday, July 1st, 2010

Aquatic insect Images from Montana and Wyoming; if you like this sort of thing let me know.



I just have time for a quick post today.

A few years ago, I prepared a collection of about 400 aquatic insect pictures to be used in by educators. Lisa Shaw, of Niobrara Conservation District, was essential in attaining funding from the Wyoming Association of Conservation Districts. The project had huge ideals: We were going have all the conservation districts send in aquatic insect specimens from all over the state of Wyoming. The idea was to have educational field trips and send in as may different bugs as possible. Some districts did just that. Some sent one person out on a solo mission, and others sent in jars or unsorted detritus (which all contained bugs).

The project was more work than expected, and my employer (at the time) withdrew support of the project, pressuring me to work on it on weekends and evenings.  Regardless, we managed to develop an impressive set of images  of the finer characteristics of aquatic insects that much of the general public never would never see otherwise. It included  whole-bug context pictures and close-ups of interesting parts… eyes, mouth-parts, gills, etc…

I would hate to have this resource fade way. I’ll post some pictures from it here from time to time.  If you are interested in attaining a copy of the document, post a comment here so I can gauge community interest in these wonderful aquatic insect pictures.

I found this Dytiscus predaceous diving beetle during my wedding–with the eager help of my nephew and brother in-law… um… from my wife… um… not so much.

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?

~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?