Tennessee Hydrologic Determination

Tennessee Hydrologic Determination (HDT) and Jurisdictional Determinations (JD) are conducted by our trained field staff and follow the Tennessee Department of Environment and Conservation Division of Water Pollution ControlGuidance For Making Hydrologic Determinations. This is required by law within the state of Tennessee under the following statute.

The following is taken from the TN statute:

Public Chapter No. 464 PUBLIC ACTS, 2009 1
STATE OF TENNESSEE
PUBLIC CHAPTER NO. 464
SENATE BILL NO. 632
Tennessee Code Annotated, Section 69-3-103, is amended by
adding the following language as new, appropriately designated subsections:
( ) “Wet weather conveyance” means, notwithstanding any other law or
rule to the contrary, man-made or natural watercourses, including natural
watercourses that have been modified by channelization:
(1) That flow only in direct response to precipitation runoff in their
immediate locality;
(2) Whose channels are at all times above the groundwater table;
(3) That are not suitable for drinking water supplies; and
(4) In which hydrological and biological analyses indicate that,
under normal weather conditions, due to naturally occurring ephemeral or
low flow there is not sufficient water to support fish, or multiple
populations of obligate lotic aquatic organisms whose life cycle includes
an aquatic phase of at least two months;

( ) “Obligate lotic aquatic organisms” means organisms that require
flowing water for all or almost all of the aquatic phase of their life cycles;

( ) “Stream” means a surface water that is not a wet weather conveyance;

( ) “Watercourse” means a man-made or natural hydrologic feature with a
defined linear channel which discretely conveys flowing water, as opposed to
sheet-flow;

Contact us or request a quote for your hydrologic determination today.

Macroinvertebrate Collection and Analysis | Aquatic Assessments

Macroinvertebrate Collection and Analysis | Aquatic Assessments – The following steps are taken from the KDOW SOP manual, and describe the methodology for collecting a multi-habitat sample in a wadeable stream:

“1. The investigator will sample a variety of non-riffle habitats with the aid of an 800 x
900 μm mesh triangular or D-frame dip net.
2. Each habitat will be sampled in at least three (3) replicates.
3. After all habitats have been sampled, the contents of the mesh wash bucket will be
composited into a glass, sampling jar with 95% ETOH.
4. The wash bucket will be picked clean of any remaining macroinvertebrates.
5. The sample jar will be labeled with appropriate information (Section 8.D.) and will be
ready for transport to the lab for analysis.
6. Each of these following habitats will be sampled:

A. Undercut Banks/Root Mats
1. These are sampled by placing a large root wad into a triangular or D-frame dip
net and shaking vigorously.
2. The contents are removed from the dip net and placed into a mesh wash bucket.
3. If undercut banks are present in both run and pool areas, each is sampled
separately with three (3) replicates.

B. Marginal Emergent Vegetation (exclusive of water willow, Justicia Americana, beds)
1. This habitat is sampled by thrusting (i.e., “jabbing”) the dip net into the
vegetation for approximately 1m, and then sweeping through the area to collect
dislodged organisms.
2. Material is then rinsed in the wash bucket and any sticks, leaves and vegetation
are thoroughly washed and inspected before discarding.

C. Bedrock or Slab-Rock Habitats
1. These habitats are sampled by placing the edge of the dip net flush on the
substrate, and disturbing approximately 0.1 m2 of area to dislodge attached
organisms.
2. Material is emptied into a wash bucket, rinsed, inspected for organisms, and
discarded.

D. Justicia americana (water willow) Beds
1. These are sampled by working the net through a 1m section in a jabbing
motion.
2. The material is then emptied into a wash bucket and any J. americana stems
are thoroughly washed, inspected and discarded.

E. Leaf Packs
1. Leaf packs are preferably collected from “conditioned” (i.e., not new-fall
material) material when possible.
2. Samples are taken from a diversity of habitats (i.e., riffles, runs and pools) and
placed into the wash bucket.
3. The material is thoroughly rinsed to dislodge organisms, inspected and
discarded.

F. Silt, Sand, and Fine Gravel
1. A U.S. No. 10 sieve is used to sort larger invertebrates (e.g., mussels,
burrowing mayflies, dragonfly larvae) from silt, sand and fine gravel by scooping
the substrate to an approximate depth of 5cm.
2. A variety of collection sites are sampled in order to obtain three (3) replicates
in each substrate type where available (silt, sand and fine gravel).

G. Aufwuchs Sample
1. Small invertebrates associated with this habitat are obtained by washing a small
amount of rocks, sticks, leaves, filamentous algae and moss into a medium-sizedbucket half filled with water.
2. The material is then elutriated and sieved with the nitex sampler/mesh.

H. Rock Picking
1. Benthic macroinvertebrates are picked from 15 rocks (large cobble/small
boulders; 5 each from riffle, run and pool).
2. Selected rocks are washed in a bucket half filled with water and then carefully
inspected to remove organisms.

I. Wood Sample
1. Pieces of submerged wood, ranging from roughly 3 to 6 meters (10 to 20 linear
feet) in length and ranging from 5–15 cm (2–6 inches) in diameter, are
individually rinsed into the wash bucket.
2. Pieces of wood are inspected for burrowers and crevice dwellers and are
removed with fine-tipped forceps.
3. Large diameter, well-aged logs should be inspected and handpicked with finetipped
forceps.”

After the samples have been processed our aquatic entomologists identify each organism and provide an analysis of the results.

To read more about our macroinvertebrate samples see here. If you would like to discuss your project or have questions contact us or request a quote.