Benthic Invertebrates


Tributary Ecosystem Health Monitoring Program 

Collection of Benthic Macro Invertebrates (Water Bugs) 


Background
 

The Tributary Ecosystem Health Monitoring Program (TEHMP) was created during the spring of 1996 because there was concern that standard water quality protocols (chemical and bacterial sampling) just show a point in time (a snapshot) and are unreliable predictors of ecosystem health. The TEHMP involves collecting and assessing stream Macro Benthic Invertebrates (water bugs). The collection method is known as biological monitoring, or biomonitoring. It is the systematic use of living organisms or their responses to assess the aquatic environment. Below are a few reasons why benthic invertebrates are excellent ecosystem indicators:

 •wide variety of species that exhibit a range of responses to independent and interactive environmental stressors 

•sedentary in nature and have a long life cycles (weeks to years) allowing temporal changes in characteristics such as abundance and age structure to be examined 

•the abundance of invertebrates, sampling equipment and the availability of easy-to-use keys for identification.

Macro Benthic Invertebrates 

There are three general taxa categories to class aquatic benthic invertebrates. Group one is pollution sensitive organisms that indicate good water quality, examples are stonefly, caddisfly, mayfly, gilled snails and water pennies. Group two is somewhat pollution tolerate organisms that are found in good to fair water quality. Examples are crayfish, sowbug, damselfly, beetle and dragonfly larvae. The third and final group is pollution tolerant - these bugs can be present in all water quality. Examples are worms, black fly larva, leeches and air breathing snails.

Group 1 (Caddisfly nymph)

Group 2 (Crayfish) Group 3 (Midge Fly Larvae)
Caddisfly nymph Cray Fish Midge Fly Larvae

Sampling Protocol used in Severn Sound 

The TEHMP assesses eight sub-watersheds within Severn Sound: Avon (1 site), Coldwater (3), Copeland (1), Hog (4), North (1), Silver (5), Sturgeon (3), and Wye River (3). Additional sites are monitored seasonally depending on projects within the watershed. Each monitoring station is evaluated once a season between the months of July/August. Two sampling protocols are used for the collection of invertebrates. The first sampling protocol is a qualitative sampling method. This involves using a hand sieve and forceps to collect invertebrates on all available habitats within a fifteen-meter stream reach. Habitats included sand, silt, gravel, rip-rap, large rocks, logs and vegetation. The second protocol is a quantitative method using a t-sampler within the riffle area of a stream because it has the highest diversity of all habitat. This protocol is used because the density of invertebrates can be calculated within a set area through the cylinder of the t-sampler. It provides valid comparisons between samples, by relative abundance and will show any species and density changes at a station. The open end of the sampler is placed into the current and the substrate inside the t-sampler is agitated for one minute and allowed too clear. The flow of the water through the t-sampler will carry any invertebrates through the net and into the catch bottle. All specimens are placed in a labeled specimen jar with seventy percent alcohol as a preservative and taken back to the lab for identification. 

After identification the invertebrates are stored for later reference. To correspond with the sampling protocols, Tidbit Temperature loggers and monthly chemistry is completed/installed at each site. The loggers are launched to record water temperature every thirty minutes from the middle of June to the end of September. The data is stored on the logger and retrieved by staff monthly. The data retrieved from the loggers is excellent for determining the thermal stability of the stream. The average water temperature at a stream is of vital importance to the survival of the stream inhabitants. 

Different species (invertebrate and fish) within a system require different temperatures for survival. For instance brook trout and brown trout require constant coldwater temperatures within a stream where sunfish/minnows can thrive in fluctuating warm water conditions. Chemistry sampling is completed through the Provincial Water Quality Monitoring Network by the Ministry of the Environment, Environmental Monitoring and Reporting Branch. The program involves collecting samples eight times within the ice-free period (monthly). 

The samples are analyzed for chloride, dissolved nutrients, ions, metals, pH, alkalinity, conductivity, suspended solids, total nutrients and turbidity. Temperature loggers and chemistry sampling will give SSEA staff additional tools to help evaluate the monitoring stations that have a low species diversity but the habitat and flow are excellent. 

Educational Component 


In the spring of 1998 a hands-on educational program was created by SSEA and local high schools. The program involves grade ten students completing a stream evaluation in four local streams. The evaluation involves collecting benthic invertebrates (qualitative method), assessing in-stream and riparian vegetation, chemical analysis (hack kits), flow measurements, temperature (air and water) and a site sketch. The benthic invertebrate samples that are collected by the students are brought back to the classroom for identification. Four sites where selected for the study:  two headwater and two mouth stations. This enabled the students to learn the different species that are present in a headwater station (unimpaired water quality) compared to mouth (impaired water quality) station.

For more information about the Tributary Ecosystem Health Monitoring Program, contact Paula Madill, Ecosystem Technologist at 705-527-5166 or by email pmadill@town.midland.on.ca 

 

 


 
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Last modified: March 08, 2010

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