10/29/2020
The use of Rapid Bioassessment Protocols in Hawaii’s streams
Part - II (Maui stream)
I had the pleasure to study streams on the islands of Maui and Oahu during my tenure in 1986 through 2004 and infancy of the Institute of Invertebrate Research Hawaii (IIRH). The IIRH has now 4 departments (centers) for additional focus and concentrations in the biological fields. The Center for Environmental Studies (CES) is more focused on environmental and climate change and findings and studies are published through that center.
The use of Rapid Bioassessment Protocols (RBP) for stream study assessment falls within the scoop and rapid use for my studies. Studies of TMDL, Visual assessments, analysis of BMI/MI, water chemistry, are among a few elements in determining the health of a given waterway or water shed area.
Part I - Oahu stream RB
Part II - Maui stream RB
Glossary of terms and abbreviations used:
BMI = Benthic Macroinvertebrates
CES = Center for Environmental Studies
IIRH = Institute of Invertebrate Research Hawaii
MI = Macroinvertebrates
RBP = Rapid Bioassessment Protocols
RB = Rapid Bioassessment
TMDL = total maximum daily load
VA = Visual Assessment
I used BMI/MI to give a rapid RB and VA of a given stream's health. Here I evaluated a stream of the Island of Oahu and the Island of Maui respectively. The stream on Oahu was centrally located in the Kalihi area and the stream on Maui was on the north-eastern coast of Hana. In early1980’s I started my RB and VA of a stream in Hana, Maui. The stream was flowing but not extreme like some of the streams that yielded Neritina (Clypeolum) granosa (Sowerby, G.B. I, 1825). The VA was impressive because the stream’s health was great. Normal water chemistry and overall turbidity; normal algae growth and surrounding vegetation. Very limited invasive species also. In fact the invasive species Physa species (pouch snail), and 2 species of the genus Melanoides: Melanoides tuberculata (O. F. Müller, 1774), Melanoides torulosa Bruguière, J.G., 1789 were not observed. During the VA and sampling I have recorded and observed the following BMI/MI species: Neripteron (Dostia) cariosum (Wood, S.V., 1828), Neripteron vespertinum (Sowerby, G.B. II, 1849) and Neripteron (Dostia) neglectum (Pease, W.H., 1861). In a previous paper I recorded the range and salinity tolerances of each species. The species with the highest range is: Neripteron (Dostia) cariosum (Wood, S.V., 1828) — able to tolerate brackish water and fresh water; the species: Neripteron vespertinum (Sowerby, G.B. II, 1849) is found only in freshwater and edge of the brackish water range; and the species: Neripteron (Dostia) neglectum (Pease, W.H., 1861) range is from the brackish waters to the edge of saltwater range. The species Neritina (Clypeolum) granosa (Sowerby, G.B. I, 1825) range in the adult stage is freshwater, but juveniles are found also at the edge of the brackish water range (Goodwin, 1991 & current research). Juveniles are smooth and round in stature with reddish-orange spots within black base color—faintly visible dorsally and noticeable from the under sides. As the species grow to adult-hood they develop bumps and recesses dorsally and the columella shield colored reddish-orange in coloration. This species has the longest life cycle—the adults climb up waterfalls upstream and deposit their eggs which in turn hatch and the larvae (veligers) flow downstream and into the open ocean where they develop into adults and make the journey back to the same stream they hatched from. This is diadromy or diadromous species of mollusks migrating between fresh and saltwater. In other words they spend part of their life cycle in freshwater and part of their life cycle in saltwater. It’s remarkable that a species in nature has the ability to identify which stream it came from or born in and venture back to that same stream to continue and complete its life cycle—truly amazing! The stream in Hana, Maui was thriving in the early 1980’s—a future visit should be conducted to evaluate its current health and conduct a RB/VA.