Stave River Water Use Plan - BC Hydro
Stave River Water Use Plan - BC Hydro
Stave River Water Use Plan - BC Hydro
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<strong>Stave</strong> <strong>River</strong> <strong>Water</strong> <strong>Use</strong> <strong>Plan</strong><br />
Monitoring Terms of Reference June 13, 2005<br />
the periphyton from Quadrant 3 will be taken before any preservative is added to the jar,<br />
and placed in a clean, glass scintillation vial. A drop or two of gluteraldehyde or dilute<br />
(4%) formaldehyde will be added to the vial and then labelled and refrigerated. Analyses<br />
of abundance of the various components of this microbial assemblage will be done first<br />
with standard microscopy at low power (200-400x) and then continued with<br />
epifluorescence microscopy. The epifluorescence microscopy technique will require a<br />
small aliquot of the sub-sample be stained with DAPI or an equivalent fluorochrome stain<br />
(Klut et. al.1989).<br />
Attached algae<br />
A few drops of acidic, Lugol's acetate preservative will be added to the remainder<br />
of the Quadrant 3 sample to preserve the periphyton biomass for microscopic analysis.<br />
The contents of the jar will be gently shaken to loosen any clumps and then allowed to<br />
settle for about 10-15 seconds, allowing some of the heavier sand/silt particles to settle<br />
from the sample. Using a wide-mouth syringe, a 2 ml sub-sample of the periphyton will<br />
be placed on a clean glass slide or depression slide for microscopic examination at low<br />
power (100-400x) magnification. If the periphyton is extremely dense, a 1 ml subsample<br />
will be placed in a 10 cc settling chamber with 9 ml of DDW added, and then<br />
examined using an inverted plankton microscope. The initial microscopic examination<br />
will be either a qualitative scan that provides information on relative abundance of major<br />
algal groups, or, by using a counting grid, a quantitative count of actual abundance of<br />
major groups. Attached siliceous diatoms are often the dominant algal assemblage in<br />
the littoral zone of oligotrophic lakes and reservoirs (also in streams), and their density is<br />
easily quantified by counts made from permanent Hyrax © slide mounts made after acid<br />
treatment of the sample (Stockner and Armstrong 1972).<br />
Primary production<br />
Primary production will be measured directly by the carbon 14 ( 14 C) method,<br />
where 14 C is inoculated into small vials with freshly scraped periphyton samples from a<br />
sample plate and incubated in situ. After a two to four-hour incubation period at the<br />
depth of the sampled plate, the contents of the vial are filtered and treated using the<br />
same protocol as described for pelagic primary production rates (Stockner and<br />
Shortreed 1985, Wetzel and Likens 1991). It should be stressed that only licensed<br />
practitioners can purchase the radioactive 14 C product needed for the inoculation<br />
procedure. As well, samplers that perform the inoculations must be certified to handle<br />
low level radioactive materials.<br />
Primary production will only be done during phase 2 of the monitor where two<br />
randomly selected blocks will be subject to the 14 C-inoculation process. Every year, 16<br />
14<br />
C based production estimates will be collected, the purpose of which is to properly<br />
calibrate the AFDW-based production estimates.<br />
<strong>BC</strong> <strong>Hydro</strong> Page 34