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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

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