Appendix G – Invertebrate Sampling MethodsMethods for sampling invertebrates include the use <strong>of</strong> artificial substrates, Surbersamplers, grab samplers and Rapid Bioassessment techniques. These are described below(modified text taken directly from the Field Sampling Procedures Manual (NJDEP,2005) and Rapid Bioassessment Protocols for Use in Streams and Wadeable Rivers(USEPA, 1999b).All benthic macroinvertebrates are preserved in 5 percent formalin (5 ml formalin/100 ml<strong>of</strong> water from which the organism was taken), with 95 percent ethanol, or isopropylalcohol. A Mason jar, or any glass or plastic wide mouth container can be used forbenthic macroinvertebrate samples.Artificial Substrates: (Hester-Dendy)These multi-plate samplers consist <strong>of</strong> eight large tempered plates separated by sevensmall plates, exposing one square foot <strong>of</strong> surface area. A hole is bored through the center<strong>of</strong> each plate. Plates are placed alternatively on a galvanized eyebolt, threaded rod ornylon cord and secured. Samplers may have a brick attached to one end to anchor thesampler to the bottom for use in shallow streams, or they may be suspended fromanchored floats in lakes and deep rivers. Used throughout, artificial substrates provideconsistency <strong>of</strong> habitat to facilitate comparison among stations. Samplers are usuallyplaced at equal intervals across a stream. However, species colonization is greatlyaffected by current velocity. When conducting a survey, care should be taken to placesubstrates at locations having similar flow characteristics. Three samplers are routinelyplaced at each sample site, although more samples may be necessary to satisfy particularstatistical criteria. When using brick-anchored samplers, additional rocks are <strong>of</strong>tennecessary to secure the sampler upright. Care should be taken not to block the plates withthe rocks and thus limit colonization. Sampling devices should be placed asinconspicuously as possible because they are prone to removal by the public. They shouldbe secured with strong nylon line (not attached to the anchor line itself). In deeper waters,suspended samplers should be placed within the euphotic zone (i.e., shallower depthswhere light penetrates) usually less than 2 meters.The samplers should be removed after a six-week colonization period. Gently remove thesampler from the water so as not to dislodge the organisms, and immediately place thesampler in a plastic tub or bucket. Anchors attached to the substrate should not be placedin the tub until any organisms on the anchor are removed and discarded. Add a smallamount <strong>of</strong> water to the tub and wash the easily removable material from the plates. Thengently scrape the top and bottom <strong>of</strong> each plate into the tub, removing the plates ascleaned. Scalpel, spatula or s<strong>of</strong>t toothbrushes are useful cleaning tools. Pour the sampleslurry through a US Standard No. 30 sieve. Additional water may be used to completelyclean the tub. Pass this through the sieve as previously described. Transfer the samplematerial from the sieve to the sample jars using forceps or a stream <strong>of</strong> water from a washbottle. Fill each jar no more than half full. Work directly over the tub so that any spilledmaterials can be recovered. Finally, inspect the tub for any remaining organisms andtransfer them to the sample jar(s). Water-resistant paper should be used for sample labelsand all information written with a s<strong>of</strong>t lead pencil. Include sample (log) number, waterbody, station, sample number, sample device, and other pertinent information.<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 119Version 1.2 8/29/12
Surber or Square-foot BottomThis sampler consists <strong>of</strong> a strong close-woven fabric (0.595-mm opening) approximately69-cm (27 in.) long held open by a one-square-foot metal frame hinged at one side toanother frame <strong>of</strong> equal size. The sampler is generally used in procuring samples in fastflowingstreams less than 1m deep. It can also be used in pools where the water depth iswadeable. Three replicate samples are usually obtained at each sampling station.Carefully place the sampler in position with the net opening facing upstream, using thecurrent to hold the net open while standing downstream and to the side <strong>of</strong> the samplingarea. By imbedding the separate two- or four-inch extensions <strong>of</strong> the horizontal frame, thesampled area will be more effectively isolated. When taking replicate samples, alwayswork across or in an upstream direction. Dislodge the rocks, stones, and other bottommaterial within the frame to a depth <strong>of</strong> at least 2 inches and collect them in the net.Remove the sampler and empty the contents into a plastic tub. Carefully inspect thelarger rocks and stones removing any organisms clinging to them, and discard the stoneswhen cleaned. Also carefully inspect the net and remove any organisms remaining. Afterthe larger materials have been inspected and removed, add a small amount <strong>of</strong> water to thetub and pour the slurry through an US Standard No. 30 sieve. This may have to berepeated several times to completely empty the tub.Grab SamplersThe Ponar, Peterson, and Ekman grab are the most commonly used grab samplers. ThePonar is similar to the Peterson except that it has side plates and a screened top to preventsampling loss. The Ekman grab is useful in sampling silt and muck in water with littlecurrent. Extreme care should be employed when locking open the jaws <strong>of</strong> the samplersbecause premature tripping will squash or sever fingers or hands. Handling by theattached line is recommended with an open sampler. Carefully lower the grab to thebottom so as not to agitate the substrate prior to sampling. Slacken the rope to trip jaws(the Ekman grab employs a messenger, which is released by the operator) and retrieve thesampler. Place it in a plastic tub or large screened bin and carefully open the samplerjaws to release the sample. The sample should be discarded if sticks or stones haveobstructed the jaws or if there is incomplete closure for any other reason. Inspect thelarger debris for organisms and discard the debris when cleaned. Filter the samplethrough a #30 sieve to remove small particles.Rapid BioassessmentBenthic rapid bioassessment procedures (RBPs) usually employ direct sampling <strong>of</strong>natural substrates, as do Surbers and grab samplers. Under certain conditions, however,such as in large rivers, the use <strong>of</strong> artificial substrates may be more appropriate for RBPanalysis. The collection procedure should provide representative samples <strong>of</strong> the benthicmacroinvertebrate fauna from comparable habitat (substrate) types at all stations in aparticular survey. Either single or multiple habitat samples can be employed dependingon which is more suitable for a particular survey. A riffle and run habitat with rocksubstrate will generally provide the most diverse community <strong>of</strong> major benthicmacroinvertebrate groups. If the stream or river is not wadeable or has an unstablesubstrate, fixed structures (e.g., submerged boulders, logs, bridges, and pilings) can<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 120Version 1.2 8/29/12
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Ecological EvaluationTechnical Guid
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6.2.1.3 Biological Sampling of Fish
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Acronyms and AbbreviationsADDAETAFA
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Executive SummaryThis document prov
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environmentally sensitive areas pur
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Figure 3-1: Flow diagram to describ
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assessment may also include evaluat
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“Hazard quotient” or “HQ” m
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parameters as specified in ERAGS (i
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71 0Sampling pointsSampling transec
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Figure 6-2: Ecological Conceptual S
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Fugacity, which is described as the
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Sample SelectionAfter completing th
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higher trophic level receptors. Lip
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Details regarding surface water tox
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COPECs. The following references ar
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multiple reference area soils repre
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In ERAs, tissue residue analyses ar
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