Hutton Creek

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Middle Rideau Subwatershed Report 2015

HUTTON CREEK CATCHMENT

The RVCA produces individual reports for ten catchments in the Middle Rideau subwatershed. Using data collected and analysed by the RVCA through its watershed monitoring and land cover classification programs, surface water quality conditions are reported for Hutton Creek along with a summary of environmental conditions for the surrounding countryside every six years.

This information is used to better understand the effects of human activity on our water resources, allows us to better track environmental change over time and helps focus watershed management actions where they are needed the most to help sustain the ecosystem services (cultural, aesthetic and recreational values; provisioning of food, fuel and clean water; regulation of erosion/natural hazard protection and water purification; supporting nutrient/water cycling and habitat provision) provided by the catchment’s lands and forests and waters (Millennium Ecosystem Assessment 2005).

The following pages of this report are a compilation of that work and contain information on surface water quality, riparian conditions, land cover, stewardship activity and hazard land and water resources protection.

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1. Catchment Facts

General Geography

• The Rideau River flows through the heart of the Middle Rideau and is a focal point for residents and visitors to the area. It extends from the outlet of Lower Rideau Lake at Poonamalie (where there is one dam and one lock) to Burritts Rapids (where there is also a dam and lock), at which point it enters the Lower Rideau on its way to Rideau Falls. The Rideau River is also an integral part of the Rideau Canal National Historic Site of Canada and is a significant tourist attraction which draws boaters, cottagers, and campers to the area
• Smiths Falls, Merrickville and Burritts Rapids are the main settlements in the Middle Rideau subwatershed. The Hutton Creek catchment is predominantly rural in character with agriculture being the main land use
• Parks Canada staff manage water levels for recreational purposes along the Rideau Canal/Waterway that flows by the catchment, ensuring 1.5 metres of draft during the navigation season. In this managed system, water levels on the Rideau Canal are manipulated by operation of numerous dams. In the Middle Rideau subwatershed, Parks Canada staff operate 9 dam and lock complexes with 13 locks for a fall of 36.2 metres over 35.6 kilometres. Water levels are maintained as close as possible to set objectives through the May to October navigation season. The levels are lowered through the rest of October and into November and held at the winter levels until the spring freshet in late March or early April naturally increases inflows to the system. To reduce the impact of the higher flows in the spring, the amount of snow water equivalent, forecast rain, ice cover, flows and levels are assessed and the dams in the Middle Rideau reach are operated accordingly to quickly pass as much water as possible. In late April and early May, the dams are gradually closed and water levels are brought up to be ready, once again, for the navigation season

Physical Geography

• All of Hutton Creek Catchment and the rest of the Middle Rideau Subwatershed primarily resides within the Smith Falls Limestone Plain. The northern part of this catchment is underlain by dolostone of the Oxford Formation; while the central catchment is underlain by the quartz sandstone and dolostone of the March Formation and a small section of the upper watershed is underlain by the Nepean Formation sandstones. The bedrock across the catchment is mainly overlain by a thin veneer of glacial sediment, referred to as ‘drift’ that is generally less than a metre in thickness; although the landscape is also dotted with organic soils and some glacial till and sand. A geologic fault likely cut through the western part of the catchment
• Eighty-six percent of the catchment lies within the Township of Elizabethtown-Kitley and 14 percent within the Township of Rideau Lakes
• Hutton Creek catchment drainage area is 62 square kilometres and occupies seven percent of the Middle Rideau subwatershed and one percent of the Rideau Valley watershed
• Parks Canada staff manage water levels for recreational purposes along the Rideau Canal/Waterway that flows by the catchment, ensuring 1.5 metres of draft during the navigation season. In this managed system, water levels on the Rideau Canal are manipulated by operation of numerous dams. In the Middle Rideau subwatershed, Parks Canada staff operate 9 dam and lock complexes with 13 locks for a fall of 36.2 metres over 35.6 kilometres. Water levels are maintained as close as possible to set objectives through the May to October navigation season. The levels are lowered through the rest of October and into November and held at the winter levels until the spring freshet in late March or early April naturally increases inflows to the system. To reduce the impact of the higher flows in the spring, the amount of snow water equivalent, forecast rain, ice cover, flows and levels are assessed and the dams in the Middle Rideau reach are operated accordingly to quickly pass as much water as possible. In late April and early May, the dams are gradually closed and water levels are brought up to be ready, once again, for the navigation season

Vulnerable Areas

• The Assessment Report developed under the Ontario Clean Water Act identifies the upper bedrock aquifer underlying all of the catchment area as a Highly Vulnerable Aquifer, although, where sediments are thicker in a local area, the vulnerability would be less. It also identifies the area of Nepean Sandstone found at the surface in this catchment as a Significant Groundwater Recharge area along with a small part of the Village of Merrickville municipal Wellhead Protection Area

Development

• Land uses in the catchment are Rural with Natural Heritage-Provincially Significant Wetland along with some Agriculture

Conditions at a Glance

Water Quality

• Surface chemistry water quality rating in Hutton Creek is “Fair” over two reporting periods (2003-2008 and 2009-2014). Elevated bacterial counts and nutrient concentrations from inflows of nutrients (from private septic systems, agricultural and residential surface water runoff) are a feature of Hutton Creek. Decreased nutrient and bacterial counts are needed to improve the overall health of the creek
• Instream biological water quality conditions at the Hutton Creek sample location range from “Fair” to “Poor” from 2010 to 2014 (using a grading scheme developed by Ontario Conservation Authorities in Ontario for benthic invertebrates) with an overall benthic invertebrate water quality rating of “Fair” determined for this period

Instream and Riparian

• In the Hutton Creek catchment, the riparian buffer (30 m. wide strip along the shoreline of all lakes and streams) is comprised of wetland (67 percent), woodland (16 percent), crop and pastureland (15 percent), roads (one percent) and settlement areas (one percent)
• Overall instream and riparian condition for the Hutton Creek catchment as assessed by the stream characterization and headwater drainage feature assessment programs show that Hutton Creek and its tributaries are in good condition. The majority of the system has low erosion levels, a healthy riparian corridor with good instream diversity of aquatic habitat
• The Hutton Creek catchment has 14 species of recreational and bait fish and is classified as having a warm/cool water thermal guild that supports the Hutton Creek/Rideau River fishery

Land Cover

• Dominant land cover is crop and pastureland (37 percent), followed by woodland (30 percent), wetland (27 percent), settlement areas (four percent) and roads (two percent). From 2008 to 2014, there was an overall change of 73 hectares (from one land cover class to another). Within the Hutton Creek catchment, change is primarily associated with the conversion of crop and pastureland to settlement (a large solar farm) and transition into woodland along with wetland encroaching into woodland
• Woodland cover in the catchment has decreased by 11 hectares between 2008 and 2014 and interior forest habitat has decreased by 26 hectares
• Wetland cover has decreased by one percent (95 ha) from pre-settlement times to the present and now occupies 27 percent of the catchment area

Other

• There are approximately 230 in-use water wells with provincial records in this catchment. While most water wells are used for domestic water supply, in this catchment, several are also used for commercial, agricultural, and public water supplies; cooling; or monitoring
• There are no active Permits to Take Water or Environmental Compliance Approvals in the catchment
• There are two bedrock aggregate licenses located in this catchment

Catchment Care

• Thirty-two stewardship projects have been completed with assistance from the RVCA’s Rural Clean Water and Tree Planting Programs (see Section 5 of this report for details)
• Hutton Creek surface water quality has been monitored by the RVCA through its Baseline Monitoring Program since 2003. The surface water quality at site HUT-02 is monitored once a month from April to November
• RVCA has been collecting benthic invertebrates in Hutton Creek at the Kitley South Elmsley Line site since 2010
• RVCA conducted a fish survey along Hutton Creek in 2014
• RVCA completed a the stream characterization survey on Hutton Creek in 2014, working upstream to the headwaters from the mouth of the creek where it empties into the Rideau River taking measurements and recording observations on instream habitat, bank stability, other attributes and preparing a temperature profile
• RVCA completed six headwater drainage feature assessments at road crossings in the Hutton Creek catchment in 2014.Tthis protocol measures zero and first order headwater drainage features and is a rapid assessment method characterizing the amount of water, sediment transport, and storage capacity within headwater drainage features
• A watershed model developed by the RVCA in 2009 was used to study the hydrologic function of wetlands in the Rideau Valley Watershed, including those found in the Hutton Creek catchment
• RVCA has built a new “berm-like” water control structure at Motts Mills, replacing the older, non-operational “stop-log” structure dating from 1952. This will now permit the manipulation of water levels in the Hutton Creek Provincially Significant Wetland (located behind the new structure), as outlined in the wetland management plan and water control structure operational plan describing that activity
• The Township of Elizabethtown-Kitley and the Township of Rideau Lakes have land use planning policies and zoning provisions - on water setbacks, frontage and naturalized shorelines and wetland protection - and in some instances use site plan control to implement these policies and provisions. Together with RVCA, these municipalities work with landowners on a case by case basis to enable new development while ensuring the scale is suitable on the lot, impacts on neighbours are minimized and development maximizes the watercourse setback
• Development in and adjacent to the Provincially Significant Wetlands in the catchment (Otter Creek, Otter Lake-Hutton Creek Complex) are subject to Ontario Regulation 174-06 (entitled “Development, Interference with Wetlands and Alterations to Shorelines and Watercourses”) that protects the hydrologic function of the wetland and also protects landowners and their property from natural hazards (flooding, fluctuating water table, unstable soils) associated with them

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2. Surface Water Quality Conditions

Surface water quality conditions in the Hutton Creek catchment are monitored by the Rideau Valley Conservation Authority’s (RVCA) Baseline Water Quality Monitoring Program. The Baseline Water Quality Program focuses on streams; data is collected for 22 parameters including nutrients (total phosphorus, total Kjeldahl nitrogen and ammonia), E. coli, metals (like aluminum and copper) and additional chemical/physical parameters (such as alkalinity, chlorides, pH and total suspended solids). Figure 1 shows the location of the monitoring site in the catchment.

Hutton Creek Water Quality

Water Quality Rating

The water quality rating for the Hutton Creek catchment is “Fair” (Table 1) as determined by the Canadian Council of Ministers of the Environment (CCME) Water Quality Index  and is largely influenced by high nutrient concentrations, metals and high bacterial counts. A "Fair" rating indicates that water quality is usually protected but is occasionally threatened or impaired; conditions sometimes depart from natural or desirable levels. Each parameter is evaluated against established guidelines to determine water quality conditions. Those parameters that frequently exceed guidelines are presented below. Analysis of the data has been broken into two periods; 2003 to 2008 and 2009 to 2014 for the stream monitoring site located on Hutton Creek (HUT-02) to examine if conditions have changed between these periods. Table 1 shows the overall rating for the monitored surface water quality site within the Hutton Creek catchment and Table 2 outlines the Water Quality Index (WQI) scores and their corresponding ratings.

Nutrients

Total phosphorus (TP) is used as a primary indicator of excessive nutrient loading and may contribute to abundant aquatic vegetation growth and depleted dissolved oxygen levels. The Provincial Water Quality Objective (PWQO) is used as the TP Guideline and states that in streams concentrations greater than 0.030 mg/l indicate an excessive amount of TP.

Total Kjeldahl nitrogen (TKN) and ammonia (NH3) are used as secondary indicators of nutrient loadings. RVCA uses a guideline of 0.500 mg/l to assess TKN^[1] and the PWQO of 0.020 mg/l to assess NH3 concentrations in Hutton Creek.

Tables 3, 4 and 5 summarize average nutrient concentrations at monitored sites within the Creek catchment and show the proportion of results that meet the guidelines.

Elevated TP results were a regular occurrence at site HUT-02; 45 percent of samples were below the guideline in the 2003-2008 period (Figure 2); this increased to 65 percent of samples in the 2009-2014 period (Figure 3). The average TP concentration increased slightly from 0.035 mg/l (2003- 2008) to 0.037 mg/l (2009-2014).

Figure 2 Total phosphorous concentrations in Hutton Creek, 2003-2008

Figure 3 Total phosphorous concentrations in Hutton Creek, 2008-2014

 

The bulk of TKN results have exceeded the guideline (Figure 4 and 5), with 15 percent of samples below the guideline in the 2003-2008 period and only 5 percent of samples below the guideline from 2009-2014. The average concentration increased from 0.846 mg/l in 2003-2008 to 0.901 in 2009-2014 mg/l (Table 4).

Figure 4 Total Kjeldahl nitrogen concentrations in Hutton Creek, 2003-2008

Figure 5 Total Kjeldahl nitrogen concentrations in Hutton Creek, 2009-2014

 

NH3 results occasionally exceeded the RVCA guideline. The proportion of results that were below the guideline were 67 percent in 2003-2008 (Figure 6); this increased to 83 percent in the 2009-2014 reporting periods (Figure 7). The average NH3 concentration decreased from 0.025 mg/l to 0.008 mg/l (Table 5). 

Figure 6 Ammonia concentrations in Hutton Creek, 2003-2008

Figure 7 Ammonia concentrations in Hutton Creek, 2008-2014

Summary

The data shows that nutrient enrichment is a feature of Hutton Creek. Average nutrient concentrations with the exception of Ammonia all slightly increased over the two reporting periods. Elevated nutrients may result in nutrient loading downstream. High nutrient concentrations can help stimulate the growth of algae blooms and other aquatic vegetation in a waterbody and deplete oxygen levels as the vegetation dies off. Best management practices such as an enhanced shoreline buffer, preventing the use of fertilizers and restricting cattle access can help to reduce nutrient enrichment in Hutton Creek. 

E. Coli

E. coli is used as an indicator of bacterial pollution from human or animal waste; in elevated concentrations it can pose a risk to human health. The PWQO of 100 colony forming units/100 millilitres (CFU/100 ml) is used. E. coli counts greater than this guideline indicate that bacterial contamination may be a problem within a waterbody.

Table 6 summarizes the geometric mean^[2] for the monitored site on Hutton Creek and shows the proportion of samples that meet the E. coli guideline of 100 CFU/100 ml. The results of the geometric mean with respect to the guideline for the two periods, 2003-2008 and 2009- 2014, are shown in Figures 8 and 9 respectively.

E. coli counts at site HUT-02 indicate a slight improvement with regard to bacterial contamination. The proportion of samples below the guideline increased from 40 percent (Figure 8) to 42 percent (Figure 9). The count at the geometric mean decreased from 136 CFU/100ml in 2003-2008 to 121 CFU/100ml (Table 6). Although the count at the geometric mean decreased, the results exceeded the guideline for both reporting periods. 

Figure 8 Geometric mean of E.coli results in Hutton Creek, 2003-2008

Figure 9 Geometric mean of E.coli results in Hutton Creek, 2009-2014

 

Summary

This data shows that bacterial contamination is a concern on Hutton Creek. There has been a slight improvement from the 2003-2008 to the 2009-2014 monitoring period, however the count at the geometric mean is above the PWQO for both monitoring periods. Properly maintaining septic systems, enhancing shoreline buffers and restricting cattle access can help to improve E.coli levels in Hutton Creek.

Metals

Of the metals routinely monitored in Hutton Creek, aluminum (Al) and iron (Fe) occasionally reported concentrations above their respective PWQOs. In elevated concentrations, these metals can have toxic effects on sensitive aquatic species.

Tables 7and 8 summarize metal concentrations at site HUT-02 and show the proportion of samples that meet guidelines. Figures 10 to 13 show metal concentrations with respect to the guidelines for the two periods of interest, 2003–2008 and 2009–2014. For Al, the PWQO is 0.075 mg/l and Fe it is 0.300 mg/l.

Results from HUT-02 shows that Al concentrations had few exceedances with 84 percent of samples below the guideline in the 2003-2008 period (Figure 10). This improved to 100 percent of samples in the 2009-2014 period (Figure 11). The average concentrations for both reporting periods were below the guideline. Aluminum results from 2003-2008 were 0.076 mg/l and from 2009-2014 the average concentration improved to 0.013 mg/l (Table 7). 

Figure 10 Average aluminum concentrations in Hutton Creek, 2003-2008

Figure 11 Average aluminum concentrations in Hutton Creek, 2009-2014

 

Iron concentrations only exceeded the PWQO guideline occassioanly during the monitoring periods. The proportion of samples below the guideline increased from 80 percent to 96 percent (Figures 12 and 13). Although there were observed exceedances, the average Fe concentration did not exceed the guideline in both monitoring periods; 0.271 mg/l in 2003-2008 and .080 mg/l in 2009-2014. 

Figure 12 Average iron concentrations in Hutton Creek, 2003-2008

Figure 13 Average iron concentrations in Hutton Creek, 2009-2014

 

Summary

Overall, a general decline in metal concentrations was observed between the two periods of interest. Efforts should continue to be made to identify pollution sources and implement best management practices to reduce any inputs such as runoff, metal alloys, fungicides and pesticides to improve overall stream health and lessen downstream impacts.

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3. Hutton Creek Riparian Conditions

Shoreline Buffer Land Cover Evaluation

The riparian or shoreline zone is that special area where the land meets the water. Well-vegetated shorelines are critically important in protecting water quality and creating healthy aquatic habitats, lakes and rivers. Natural shorelines intercept sediments and contaminants that could impact water quality conditions and harm fish habitat in streams. Well established buffers protect the banks against erosion, improve habitat for fish by shading and cooling the water and provide protection for birds and other wildlife that feed and rear young near water. A recommended target (from Environment Canada’s Guideline: How Much Habitat is Enough?) is to maintain a minimum 30 metre wide vegetated buffer along at least 75 percent of the length of both sides of rivers, creeks and streams.

Figure 14 shows the extent of the naturally vegetated riparian zone along a 30 metre wide strip of shoreline of Hutton Creek and its tributaries. This information is derived from a dataset developed by the RVCA’s Land Cover Classification Program through heads-up digitization of 20cm DRAPE ortho-imagery at a 1:4000 scale, which details the catchment landscape using 10 land cover classes.

This analysis shows that the riparian buffer in the Hutton Creek catchment is comprised of wetland (67 percent), woodland (16 percent), crop and pastureland (15 percent), roads (one percent) and settlement areas (one percent). Additional statistics for the Hutton Creek catchment are presented in Table 9 and show that there has been very little change in shoreline cover from 2008 to 2014.

Hutton Creek Overbank Zone

Riparian Buffer Width Evaluation

Figure 15 demonstrates the buffer conditions of the left and right banks separately.  Hutton Creek had a buffer of greater than 30 meters along 85 percent of the right bank and 89 percent of the left bank.

Adjacent Land Use

The RVCA’s Stream Characterization Program identifies eight different land uses beside Hutton Creek (Figure 16). Surrounding land use is considered from the beginning to end of the survey section (100m) and up to 100m on each side of the creek. Land use outside of this area is not considered for the surveys but is nonetheless part of the subwatershed and will influence the creek. Natural areas made up 88 percent of the stream, characterized by wetlands, forest, scrubland and meadow. The remaining land use consisted of pasture, active agriculture, recreational and infrastructure in the form of road crossings.

Hutton Creek Shoreline Zone

Instream Erosion

Erosion is a normal, important stream process and may not affect actual bank stability; however, excessive erosion and deposition of sediment within a stream can have a detrimental effect on important fish and wildlife habitat.  Poor bank stability can greatly contribute to the amount of sediment carried in a waterbody as well as loss of bank vegetation due to bank failure, resulting in trees falling into the stream and the potential to impact instream migration.   Figure 17 shows low levels of erosion was observed along Hutton Creek.

Undercut Stream Banks

Undercut banks are a normal and natural part of stream function and can provide excellent refuge areas for fish. Figure 18 shows that Hutton Creek had low levels of undercut banks.

Stream Shading

Grasses, shrubs and trees all contribute towards shading a stream. Shade is important in moderating stream temperature, contributing to food supply and helping with nutrient reduction within a stream. Figure 19 shows variable stream shading conditions ranging from low levels to high levels along Hutton Creek.

Instream Woody Debris

Figure 20 shows that the majority of Hutton Creek had low to moderate levels of instream woody debris in the form of branches and trees. Instream woody debris is important for fish and benthic invertebrate habitat, by providing refuge and feeding areas.

Overhanging Trees and Branches

Figure 21 shows low to high levels of overhanging branches and trees along Hutton Creek. Overhanging branches and trees provide a food source, nutrients and shade which helps to moderate instream water temperatures.

Anthropogenic Alterations

Figure 22 shows 94 percent of Hutton Creek remains “unaltered” with no anthropogenic alterations.   Six percent of Hutton Creek was classified as natural with minor anthropogenic changes in the form of road crossings. 

Hutton Creek Instream Aquatic Habitat

Benthic Invertebrates

Freshwater benthic invertebrates are animals without backbones that live on the stream bottom and include crustaceans such as crayfish, molluscs and immature forms of aquatic insects. Benthos represent an extremely diverse group of aquatic animals and exhibit wide ranges of responses to stressors such as organic pollutants, sediments and toxicants, which allows scientists to use them as bioindicators.  As part of the Ontario Benthic Biomonitoring Network (OBBN), the RVCA has been collecting benthic invertebrates at the Kitley South Elmsley Line site on Hutton Creek since 2010. Monitoring data is analyzed for each sample site and the results are presented using the Family Biotic Index, Family Richness and percent Ephemeroptera, Plecoptera and Trichoptera.

Hilsenhoff Family Biotic Index

The Hilsenhoff Family Biotic Index (FBI) is an indicator of organic and nutrient pollution and provides an estimate of water quality conditions for each site using established pollution tolerance values for benthic invertebrates. The Hutton Creek sample location was added to the OBBN network in 2010.  As a result FBI results for Hutton Creek are limited to the most recent reporting period of 2010 to 2014.  “Poor” to “Good” water quality conditions were observed at the Hutton Creek sample location for the period of 2010 to 2014 (Fig.23) using a grading scheme developed by Conservation Authorities in Ontario for benthic invertebrates.

Family Richness

Family Richness measures the health of the community through its diversity and increases with increasing habitat diversity suitability and healthy water quality conditions. Family Richness is equivalent to the total number of benthic invertebrate families found within a sample.   Hutton Creek is reported to have “Fair” to “Good” levels for family richness (Fig.24).

EPT

Ephemeroptera (Mayflies), Plecoptera (Stoneflies), and Trichoptera (Caddisflies) are species considered to be very sensitive to poor water quality conditions. High abundance of these organisms is generally an indication of good water quality conditions at a sample location.  The community structure is mixed with species that are sensitive, moderately tolerant and tolerant to poor water quality conditions.  As a result, the EPT indicates that Hutton Creek is reported to have “Poor” to “Fair” water quality (Fig.25) from 2010 to 2014.

Conclusion

Overall aquatic habitat conditions from a benthic invertebrate perspective for Hutton Creek range from “Fair” to “Poor” from 2010 to 2014.

Habitat Complexity

Streams are naturally meandering systems and move over time; there are varying degrees of habitat complexity, depending on the creek. Examples of habitat complexity include variable habitat types such as pools and riffles as well as substrate variability and woody debris structure.  A high percentage of habitat complexity (heterogeneity) typically increases the biodiversity of aquatic organisms within a system. Seventy one percent of Hutton Creek was considered heterogeneous, as shown in Figure 26.

Instream Substrate

Diverse substrate is important for fish and benthic invertebrate habitat because some species have specific substrate requirements and for example will only reproduce on certain types of substrate.  Figure 27 shows that 25 percent of the substrate observed on Hutton Creek was dominated by cobble.  Overall substrate conditions were highly variable along Hutton Creek.  Figure 28 shows the dominant substrate type observed for each section surveyed along Hutton Creek.

Cobble and Boulder Habitat

Boulders create instream cover and back eddies for large fish to hide and/or rest out of the current.  Cobble provides important spawning habitat for certain fish species like walleye and various shiner species who are an important food source for larger fish.  Cobble can also provide habitat conditions for benthic invertebrates that are a key food source for many fish and wildlife species.  Figure 29 shows where cobble and boulder substrate are found in Hutton Creek.

Instream Morphology

Pools and riffles are important habitat features for fish. Riffles are areas of agitated water and they contribute higher dissolved oxygen to the stream and act as spawning substrate for some species of fish, such as walleye. Pools provide shelter for fish and can be refuge pools in the summer if water levels drop and water temperature in the creek increases. Pools also provide important over wintering areas for fish. Runs are usually moderately shallow, with unagitated surfaces of water and areas where the thalweg (deepest part of the channel) is in the center of the channel.  Figure 31 shows where the riffle habitats are located along Hutton Creek.

Figure 30 shows that Hutton Creek is variable; 73 percent consists of runs, 22 percent riffles and 5 percent pools.

Vegetation Type

Instream vegetation provides a variety of functions and is a critical component of the aquatic ecosystem.  For example emergent plants along the shoreline can provide shoreline protection from wave action and important rearing habitat for species of waterfowl.  Submerged plants provide habitat for fish to find shelter from predator fish while they feed.  Floating plants such as water lilies shade the water and can keep temperatures cool while reducing algae growth.  The dominant vegetation type recorded at forty- eight percent consisted of algae. Figure 32 depicts the plant community structure for Hutton Creek. Hutton Creek had high levels of diversity for instream vegetation. Figure 33 shows the dominant vegetation type observed for each section surveyed along Hutton Creek.

Instream Vegetation Abundance

Instream vegetation is an important factor for a healthy stream ecosystem. Vegetation helps to remove contaminants from the water, contributes oxygen to the stream, and provides habitat for fish and wildlife. Too much vegetation can also be detrimental. Figure 34 demonstrates that Hutton Creek had sections dominated by low levels of instream vegetation for forty eight percent of its length. This is likely due in large part to high amounts of bedrock substrate along the system which does not allow aquatic vegetation to become established.

Invasive Species

Invasive species can have major implications on streams and species diversity. Invasive species are one of the largest threats to ecosystems throughout Ontario and can out compete native species, having negative effects on local wildlife, fish and plant populations. Seventy seven percent of the sections surveyed along Hutton Creek had invasive species (Figure 35). The invasive species observed in Hutton Creek were European frogbit, purple loosestrife, glossy and common buckthorn, and Manitoba maple.  Figure 36 shows the frequency of the invasive species observed along Hutton Creek.

Hutton Creek Water Chemistry

Water Chemistry Measurement

During the stream characterization survey, a YSI probe is used to collect water chemistry information.  Dissolved oxygen, conductivity and pH are measured at the start and end of each section.

Dissolved Oxygen

Dissolved oxygen is a measure of the amount of oxygen dissolved in water. The Canadian Environmental Quality Guidelines of the Canadian Council of Ministers of the Environment (CCME) suggest that for the protection of aquatic life the lowest acceptable dissolved oxygen concentration should be 6 mg/L for warmwater biota and 9.5 mg/L for coldwater biota (CCME, 1999).  Figure 37 shows that the dissolved oxygen in Hutton Creek was within the threshold for warmwater biota in most reaches of the system.  The average dissolved oxygen levels observed within the main stem of Hutton Creek was 7.34 mg/L which is within the recommended levels for warmwater biota. 

Conductivity

Conductivity in streams is primarily influenced by the geology of the surrounding environment, but can vary drastically as a function of surface water runoff. Currently there are no CCME guideline standards for stream conductivity, however readings which are outside the normal range observed within the system are often an indication of unmitigated discharge and/or stormwater input. The average conductivity observed within the main stem of Hutton Creek was 288 µs/cm. Figure 38 shows that the conductivity readings for Hutton Creek.

pH

Based on the PWQO for pH, a range of 6.5 to 8.5 should be maintained for the protection of aquatic life. Average pH values for Hutton Creek averaged 7.8 thereby meeting the provincial standard.

Thermal Regime

Many factors can influence fluctuations in stream temperature, including springs, tributaries, precipitation runoff, discharge pipes and stream shading from riparian vegetation. Water temperature is used along with the maximum air temperature (using the Stoneman and Jones method) to classify a watercourse as either warm water, cool water or cold water. Analysis of the data collected indicates that Hutton Creek is classified as a warm water system with cool to warm water reaches. 

Each point on the graph represents a temperature that meets the following criteria:

• Sampling dates between July 1st and September 7th
• Sampling date is preceded by two consecutive days above 24.5 °C, with no rain
• Water temperatures are collected at 4pm
• Air temperature is recorded as the max temperature for that day

Groundwater

Groundwater discharge areas can influence stream temperature, contribute nutrients, and provide important stream habitat for fish and other biota. During stream surveys, indicators of groundwater discharge are noted when observed. Indicators include: springs/seeps, watercress, iron staining, significant temperature change and rainbow mineral film.  Figure 42 shows areas where one or more of the above groundwater indicators were observed during stream surveys and headwater assessments.

Headwaters Drainage Features Assessment 

The RVCA Stream Characterization program assessed Headwater Drainage Features for the Middle Rideau subwatershed in 2014. This protocol measures zero, first and second order headwater drainage features (HDF).  It is a rapid assessment method characterizing the amount of water, sediment transport, and storage capacity within headwater drainage features (HDF). RVCA is working with other Conservation Authorities and the Ministry of Natural Resources and Forestry to implement the protocol with the goal of providing standard datasets to support science development and monitoring of headwater drainage features.  An HDF is a depression in the land that conveys surface flow. Additionally, this module provides a means of characterizing the connectivity, form and unique features associated with each HDF (OSAP Protocol, 2013). In 2014 the program sampled 6 sites at road crossings in the Hutton Creek catchment area shown in Figure 43.

Headwater Feature Type

The headwater sampling protocol assesses the feature type in order to understand the function of each feature.  The evaluation includes the following classifications: defined natural channel, channelized or constrained, multi-thread, no defined feature, tiled, wetland, swale, roadside ditch and pond outlet.  By assessing the values associated with the headwater drainage features in the catchment area we can understand the ecosystem services that they provide to the watershed in the form of hydrology, sediment transport, and aquatic and terrestrial functions.  The Hutton Creek catchment is dominated by natural channel and wetland headwater drainage features.  Figure 44 shows the feature type of the primary feature at the sampling locations.

Headwater Feature Flow Type

The observed flow condition within headwater drainage features can be highly variable depending on timing relative to the spring freshet, recent rainfall, soil moisture, etc.  Flow conditions are assessed in the spring and in the summer to determine if features are perennial and flow year round, if they are intermittent and dry up during the summer months or if they are ephemeral systems that do not flow regularly and generally respond to specific rainstorm events or snowmelt.  Flow conditions in headwater systems can change from year to year depending on local precipitation patterns.  Figure 45 shows the observed flow conditions at the sampling locations in the Hutton Creek catchment.

Feature Channel Modifications

Channel modifications were assessed at each headwater drainage feature sampling location.  Modifications include channelization, dredging, hardening and realignments.  The sampling locations for the Hutton Creek catchment area were classified as having no channel modifications.  Figure 46 shows the channel modifications observed at the sampling locations for Hutton Creek.

Headwater Feature Vegetation

Headwater feature vegetation evaluates the type of vegetation that is found within the drainage feature.  The type of vegetated within the channel influences the aquatic and terrestrial ecosystem values that the feature provides.  For some types of headwater features the vegetation within the feature plays a very important role in flow and sediment movement and provides wildlife habitat.  The following classifications are evaluated no vegetation, lawn, wetland, meadow, scrubland and forest.  Figure 47. Depicts the dominant vegetation observed at the sampled headwater sites in the Hutton Creek catchment.

Headwater Feature Riparian Vegetation

Headwater riparian vegetation evaluates the type of vegetation that is found along the adjacent lands of a headwater drainage feature.  The type of vegetation within the riparian corridor influences the aquatic and terrestrial ecosystem values that the feature provides to the watershed.  The majority of the sample locations in Hutton Creek were dominated by natural vegetation in the form of scrubland, forest and wetland vegetation.  Figure 48 shows the type of riparian vegetation observed at the sampled headwater sites in the Hutton Creek catchment.

Headwater Feature Sediment Deposition

Assessing the amount of recent sediment deposited in a channel provides an index of the degree to which the feature could be transporting sediment to downstream reaches (OSAP, 2013).  Evidence of excessive sediment deposition might indicate the requirement to follow up with more detailed targeted assessments upstream of the site location to identify potential best management practices to be implemented.  Conditions ranged from no deposition observed to a site with substantial deposition recorded.  Overall most sites had minimal to moderate levels of sediment deposition.  Figure 49 Depicts the degree of sediment deposition observed at the sampled headwater sites in the Hutton Creek catchment.

Headwater Feature Upstream Roughness

Feature roughness will provide a measure of the amount of materials within the bankfull channel that could slow down the velocity of water flowing within the headwater feature (OSAP, 2013).  Materials on the channel bottom that provide roughness include vegetation, woody debris and boulders/cobble substrates.  Roughness can provide benefits in mitigating downstream erosion on the headwater drainage feature and the receiving watercourse by reducing velocities.  Roughness also provides important habitat conditions to aquatic organisms. All of the sample locations in the Hutton Creek catchment area had moderate levels of feature roughness.  Figure 50 shows the feature roughness conditions at the sampling locations in the Hutton Creek catchment.

Fish Community

The Hutton Creek catchment is classified as a mixed community of warm and cool water recreational and baitfish fishery with 14 species observed.  Table 10 lists those species observed in the catchment (Source: MNR/RVCA).  Figure 51 shows the sampling locations along Hutton Creek.

Migratory Obstructions

It is important to know locations of migratory obstructions because these can prevent fish from accessing important spawning and rearing habitat. Migratory obstructions can be natural or manmade, and they can be permanent or seasonal. Figure 52 shows that Hutton Creek had two debris jams at the time of the survey in 2014.  The Motts Mills dam supports a headwater provincially significant wetland which provides enormous ecological benefits to the catchment area.

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4. Land Cover

Land cover and any change in coverage that has occurred over a six year period is summarized for the Hutton Creek catchment using spatially continuous vector data representing the catchment during the spring of 2008 and 2014. This dataset was developed by the RVCA through heads-up digitization of 20cm DRAPE ortho-imagery at a 1:4000 scale and details the surrounding landscape using 10 land cover classes.

As shown in Table 11, the dominant land cover types in the catchment through 2008 and 2014 were crop and pastureland along with woodland and wetland.

From 2008 to 2014, there was an overall change of 73 hectares (from one land cover class to another). Change within the Hutton Creek catchment is primarily associated with the conversion of crop and pastureland to settlement (i.e., a large solar farm) and transition into woodland along with wetland encroaching into woodland (see Figure 53 for the location of the major changes).

Table 12 shows the type of land cover change that has taken place between land cover classes/types from 2008 to 2014. Overall, the net area of ‘crop and pastureland’ change (loss) is small at 41 hectares relative to the remaining area of ‘crop and pastureland’ in the catchment (as of 2014). Similarly, the net area of woodland change (loss) is small at 15 hectares relative to the remaining area of woodland in the catchment (as of 2014).

Woodland Cover

In the Environment Canada Guideline (Third Edition) entitled “How Much Habitat Is Enough?” (hereafter referred to as the “Guideline”) the opening narrative under the Forest Habitat Guidelines section states that prior to European settlement, forest was the predominant habitat in the Mixedwood Plains ecozone. The remnants of this once vast forest now exist in a fragmented state in many areas (including the Rideau Valley watershed) with woodland patches of various sizes distributed across the settled landscape along with higher levels of forest cover associated with features such as the Frontenac Axis (within the on-Shield areas of the Rideau Lakes and Tay River subwatersheds). The forest legacy, in terms of the many types of wildlife species found, overall species richness, ecological functions provided and ecosystem complexity is still evident in the patches and regional forest matrices (found in the Middle Rideau subwatershed and elsewhere in the Rideau Valley watershed). These ecological features are in addition to other influences which forests have on water quality and stream hydrology including reducing soil erosion, producing oxygen, storing carbon along with many other ecological services that are essential not only for wildlife but for human well-being.

The Guideline also notes that forests provide a great many habitat niches that are in turn occupied by a great diversity of plant and animal species. They provide food, water and shelter for these species - whether they are breeding and resident locally or using forest cover to help them move across the landscape. This diversity of species includes many that are considered to be species at risk. Furthermore, from a wildlife perspective, there is increasing evidence that the total forest cover in a given area is a major predictor of the persistence and size of bird populations, and it is possible or perhaps likely that this pattern extends to other flora and fauna groups. The overall effect of a decrease in forest cover on birds in fragmented landscapes is that certain species disappear and many of the remaining ones become rare, or fail to reproduce, while species adapted to more open and successional habitats, as well as those that are more tolerant to human-induced disturbances in general, are able to persist and in some cases thrive. Species with specialized-habitat requirements are most likely to be adversely affected. The overall pattern of distribution of forest cover, the shape, area and juxtaposition of remaining forest patches and the quality of forest cover also play major roles in determining how valuable forests will be to wildlife and people alike.

The current science generally supports minimum forest habitat requirements between 30 and 50 percent, with some limited evidence that the upper limit may be even higher, depending on the organism/species phenomenon under investigation or land-use/resource management planning regime being considered/used.

As shown in Figure 54, 33 percent of the Hutton Creek catchment contains 1825 hectares of upland forest and 221 hectares of lowland forest (treed swamps) versus the 34 percent of woodland cover in the Middle Rideau subwatershed. This is greater than the 30 percent of forest cover that is identified as the minimum threshold required to sustain forest birds according to the Guideline and which may only support less than one half of potential species richness and marginally healthy aquatic systems. When forest cover drops below 30 percent, forest birds tend to disappear as breeders across the landscape.

Woodland (Patch) Size

According to the Ministry of Natural Resources’ Natural Heritage Reference Manual (Second Edition), larger woodlands are more likely to contain a greater diversity of plant and animal species and communities than smaller woodlands and have a greater relative importance for mobile animal species such as forest birds.

Bigger forests often provide a different type of habitat. Many forest birds breed far more successfully in larger forests than they do in smaller woodlots and some rely heavily on forest interior conditions. Populations are often healthier in regions with more forest cover and where forest fragments are grouped closely together or connected by corridors of natural habitat. Small forests support small numbers of wildlife. Some species are “area-sensitive” and tend not to inhabit small woodlands, regardless of forest interior conditions. Fragmented habitat also isolates local populations, especially small mammals, amphibians and reptiles with limited mobility. This reduces the healthy mixing of genetic traits that helps populations survive over the long run (Conserving the Forest Interior. Ontario Extension Notes, 2000).

The Environment Canada Guideline also notes that for forest plants that do not disperse broadly or quickly, preservation of some relatively undisturbed large forest patches is needed to sustain them because of their restricted dispersal abilities and specialized habitat requirements and to ensure continued seed or propagation sources for restored or regenerating areas nearby.

The Natural Heritage Reference Manual continues by stating that a larger size also allows woodlands to support more resilient nutrient cycles and food webs and to be big enough to permit different and important successional stages to co-exist. Small, isolated woodlands are more susceptible to the effects of blowdown, drought, disease, insect infestations, and invasions by predators and non-indigenous plants. It is also known that the viability of woodland wildlife depends not only on the characteristics of the woodland in which they reside, but also on the characteristics of the surrounding landscape where the woodland is situated. Additionally, the percentage of forest cover in the surrounding landscape, the presence of ecological barriers such as roads, the ability of various species to cross the matrix surrounding the woodland and the proximity of adjacent habitats interact with woodland size in influencing the species assemblage within a woodland.

In the Hutton Creek catchment (in 2014), 69 (37 percent) of the 184 woodland patches are very small, being less than one hectare in size. Another 94 (51 percent) of the woodland patches ranging from one to less than 20 hectares in size tend to be dominated by edge-tolerant bird species. The remaining 21 (12 percent of) woodland patches range between 21 and 214 hectares in size. Sixteen of these patches contain woodland between 20 and 100 hectares and may support a few area-sensitive species and some edge intolerant species, but will be dominated by edge tolerant species.

Conversely, five (three percent) of the 184 woodland patches in the drainage area exceed the 100 plus hectare size needed to support most forest dependent, area sensitive birds and are large enough to support approximately 60 percent of edge-intolerant species. One patch tops 200 hectares, which according to the Environment Canada Guideline will support 80 percent of edge-intolerant forest bird species (including most area sensitive species) that prefer interior forest habitat conditions.

Table 13 presents a comparison of woodland patch size in 2008 and 2014 along with any changes that have occurred over that time. A decrease (of 11 ha) has been observed in the overall woodland patch area between the two reporting periods with most change occurring in the 100 to 200 and greater than 200 hectare woodland patch size class ranges.

Forest Interior

The forest interior is habitat deep within woodlands. It is a sheltered, secluded environment away from the influence of forest edges and open habitats. Some people call it the “core” or the “heart” of a woodland. The presence of forest interior is a good sign of woodland health, and is directly related to the woodland’s size and shape. Large woodlands with round or square outlines have the greatest amount of forest interior. Small, narrow woodlands may have no forest interior conditions at all. Forest interior habitat is a remnant natural environment, reminiscent of the extensive, continuous forests of the past. This increasingly rare forest habitat is now a refuge for certain forest-dependent wildlife; they simply must have it to survive and thrive in a fragmented forest landscape (Conserving the Forest Interior. Ontario Extension Notes, 2000).

The Natural Heritage Reference Manual states that woodland interior habitat is usually defined as habitat more than 100 metres from the edge of the woodland and provides for relative seclusion from outside influences along with a moister, more sheltered and productive forest habitat for certain area sensitive species. Woodlands with interior habitat have centres that are more clearly buffered against the edge effects of agricultural activities or more harmful urban activities than those without.

In the Hutton Creek catchment (in 2014), the 184 woodland patches contain 91 forest interior patches (Figure 14) that occupy two percent (151 ha.) of the catchment land area (which is less than the five percent of interior forest in the Middle Rideau Subwatershed). This is below the ten percent figure referred to in the Environment Canada Guideline that is considered to be the minimum threshold for supporting edge intolerant bird species and other forest dwelling species in the landscape.

Most patches (87) have less than 10 hectares of interior forest, 61 of which have small areas of interior forest habitat less than one hectare in size. The remaining 4 patches contain interior forest ranging between 12 and 19 hectares in area.

Between 2008 and 2014, there has been a change in the number of woodland patches containing smaller areas of interior habitat (Table 14). For example, there has been an increase of 48 woodlands containing less than one hectare of interior forest over this and 15 woodlands with one to 10 hectares of interior habitat.

Wetland Cover

Wetlands are habitats forming the interface between aquatic and terrestrial systems. They are among the most productive and biologically diverse habitats on the planet. By the 1980s, according to the Natural Heritage Reference Manual, 68 percent of the original wetlands south of the Precambrian Shield in Ontario had been lost through encroachment, land clearance, drainage and filling.

Wetlands perform a number of important ecological and hydrological functions and provide an array of social and economic benefits that society values. Maintaining wetland cover in a watershed provides many ecological, economic, hydrological and social benefits that are listed in the Reference Manual and which may include:

• contributing to the stabilization of shorelines and to the reduction of erosion damage through the mitigation of water flow and soil binding by plant roots
• mitigating surface water flow by storing water during periods of peak flow (such as spring snowmelt and heavy rainfall events) and releasing water during periods of low flow (this mitigation of water flow also contributes to a reduction of flood damage)
• contributing to an improved water quality through the trapping of sediments, the removal and/or retention of excess nutrients, the immobilization and/or degradation of contaminants and the removal of bacteria
• providing renewable harvesting of timber, fuel wood, fish, wildlife and wild rice
• contributing to a stable, long-term water supply in areas of groundwater recharge and discharge
• providing a high diversity of habitats that support a wide variety of plants and animals
• acting as “carbon sinks” making a significant contribution to carbon storage
• providing opportunities for recreation, education, research and tourism

Historically, the overall wetland coverage within the Great Lakes basin exceeded 10 percent, but there was significant variability among watersheds and jurisdictions, as stated in the Environment Canada Guideline. In the Rideau Valley Watershed, it has been estimated that pre-settlement wetland cover averaged 35 percent using information provided by Ducks Unlimited Canada (2010) versus the 21 percent of wetland cover existing in 2014 derived from DRAPE imagery analysis.

Using the same dataset, it is estimated that pre-settlement (historic) wetland cover averaged 32 percent in the Middle Rideau subwatershed versus the 27 percent of cover existing in 2014. This decline in wetland cover is also evident in the Hutton Creek catchment (as seen in Figure 55) where there has been a one percent decrease in the area of wetland cover from pre-settlement times to the present (as summarized in Table 15).

While there has been a reported decrease in wetland cover in the Hutton Creek catchment from pre-settlement times, the remaining wetland cover in 2014 remains above the ecological thresholds cited in the Environment Canada Guideline. Nonetheless, in order to maintain critical hydrological, ecological functions along with related recreational and economic benefits provided by these wetland habitats in the catchment, a “no net loss” of currently existing wetlands should be employed to ensure the continued provision of tangible benefits accruing from them for landowners and surrounding communities.

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5. Stewardship and Protection

The RVCA and its partners are working to protect and enhance environmental conditions in the Middle Rideau Subwatershed. Figure 56 shows the location of all stewardship projects completed in the Hutton Creek catchment along with sites identified for potential shoreline restoration.

Rural Clean Water Projects

From 2009 to 2014, three septic system replacements were completed. Between 2003 and 2008, two well upgrades, two livestock fencing projects, two fuel storage and handling facilities, two education initiatives, one septic system replacement and one clean water diversion were carried out. Prior to 2003, seven livestock fencing projects, one manure storage facility and one milkhouse wastewater treatment facility were completed. Total value of all 22 projects is $178,001 with $103,625 of that amount funded through grant dollars from the RVCA.

Tree Planting Projects

The location of RVCA Tree Planting Program projects is shown in Figure 56. From 2009 to 2014, 5,100 trees were planted at two sites. Between 2003 and 2008, 15,826 trees were planted at two sites and prior to 2003, 19,310 trees were planted at six sites, resulting in the reforestation of 20 hectares. Total value of all ten projects is $110,881 with $36,509 of that amount coming from various fundraising sources.

Through the RVCA Butternut Recovery Program, an additional 30 butternut trees were planted in the Hutton Creek catchment between 2003 and 2008, as part of efforts to introduce healthy seedlings from tolerant butternuts into various locations across Eastern Ontario.

Valley, Stream, Wetland and Hazard Land Regulation

The Hutton Creek catchment covers 62 square kilometres with 20.6 square kilometres (or 33 percent) of the drainage area being within the regulation limit of Ontario Regulation 174/06 (Figure 57), giving protection to wetland areas and river or stream valleys that are affected by flooding and erosion hazards.

Wetlands occupy 16.6 sq. km. (or 27 percent) of the catchment. Of these wetlands, 11 sq. km (or 66 percent) are designated as provincially significant and included within the RVCA regulation limit. This leaves the remaining 5.6 sq. km (or 34 percent) of wetlands in the catchment outside the regulated area limit.

Of the 85.4 kilometres of stream in the catchment, regulation limit mapping has been plotted along 47.5 kilometers of streams (representing 56 percent of all streams in the catchment). Some of these regulated watercourses (39.6 km or 46 percent of all streams) flow through regulated wetlands; the remaining 8 km (or 17 percent) of regulated streams are located outside of those wetlands. Plotting of the regulation limit on the remaining 37.9 km (or 44 percent) of streams requires identification of flood and erosion hazards and valley systems.

Within the regulation limit, “development” and “site alteration” require RVCA permission. The “alteration to waterways” provision of Ontario Regulation 174/06 applies to all watercourses.

Vulnerable Drinking Water Areas

The Hutton Creek drainage catchment is considered to have a Highly Vulnerable Aquifer. This means that the nature of the overburden (thin soils, fractured bedrock) does not provide a high level of protection for the underlying groundwater making the aquifer more vulnerable to contaminants released on the surface. The Mississippi-Rideau Source Protection Plan includes policies that focus on the protection of groundwater region-wide due to the fact that most of the region, which encompasses the Mississippi and Rideau watersheds, is considered Highly Vulnerable Aquifer. For detailed maps and policies that have been developed to protect drinking water sources, please go to the Mississippi-Rideau Source Protection Region website at www.mrsourcewater.ca to view the Mississippi-Rideau Source Protection Plan.

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6. Challenges/Issues

Water Quality

• Surface chemistry water quality along Hutton Creek is “Fair” over two reporting periods (2003-2008 and 2009-2014) as determined by surface water chemistry data. Frequent exceedances of nutrients and E. coli as well as occasional exceedances of aluminum and iron contributed to the rating. Nutrient concentrations have increased in the 2009-2014 reporting period
• Instream biological water quality conditions at the Hutton Creek sample location range from “Fair” to “Poor” from 2010 to 2014 (using a grading scheme developed by Ontario Conservation Authorities in Ontario for benthic invertebrates) with an overall benthic invertebrate water quality rating of “Fair” determined for this period

Shorelines

• Emerald ash borer poses a significant threat to the ecology of the subwatershed, given the prominence of ash trees along shorelines and in riparian and wetland areas. Many tree stands are predominantly ash and with their anticipated loss, it is unclear what will replace them and the overall effect of their collective demise on the physical and natural functions/values they provide for erosion, water quality and fish and wildlife habitat protection

Land Cover

• The catchment contains 560 ha of unevaluated wetland (occupying nine percent of its total area) that provides many important social, hydrological, biological and ecological functions/services. Although not under imminent threat from development activity, they do remain vulnerable to drainage and land clearing activities in the absence of any regulatory and planning controls that would otherwise protect them​

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7. Opportunities/Actions

Water Quality

• Investigate the source of possible pollutants along Hutton Creek and consider implementing measures to reduce nutrient and bacterial loadings
• Implement agricultural and residential best management practices to address the elevated nutrient concentrations, high bacteria counts and occasional metal exceedances on Hutton Creek by restricting livestock access to the creek, limiting the use of fertilizers and pesticide applications and improving or maintaining a shoreline buffer
• Continue to offer the suite of water quality improvement projects provided by the Rideau Valley Rural Clean Water Program to landowners
• Continue to protect Hutton Creek and its tributaries through implementation of municipal and agency land use planning and development policies and practices

Shorelines/Headwaters

• Continue to promote the Rideau Valley Shoreline Naturalization and Tree Planting Programs to landowners
• RVCA and its partners (Townships of Elizabethtown-Kitley and Rideau Lakes) are to continue educating landowners about the value and importance of headwater drainage features, natural shorelines and waterfront property best management practices with respect to shoreline use and development, septic system installation and maintenance and shoreline vegetation retention and enhancement
• Protect the riparian buffer along the shoreline of Hutton Creek and other catchment streams (headwaters) during the development approvals process through adherence to and enforcement of municipal land-use policies and zoning standards
• Target shoreline restoration at sites identified in this report (shown as “Other riparian land cover” in Figure 14) and explore other restoration and enhancement opportunities along Hutton Creek and its tributaries

Development

• Collectively work with approval authorities (Townships of Elizabethtown-Kitley and Rideau Lakes, Conservation Authority) to consistently implement current land use planning and development policies for water quality and shoreline protection adjacent to Hutton Creek and other catchment streams (e.g., a minimum 30 metre development setback from water)
• Explore ways and means to more effectively enforce and implement conditions of land-use planning and development approval to achieve net environmental gains (particularly with respect to rehabilitating or protecting naturally vegetated shorelines and water quality)
• Municipalities and agencies are encouraged to strengthen natural heritage and water resources official plan policies and zoning provisions (water setbacks, frontage and naturalized shorelines and wetland protection) where deemed appropriate
• Utilize RVCA subwatershed and catchment reports to help develop/revise official plan policies to protect surface water resources and the natural environment (including woodlands, wetlands and shoreline cover)
• Consider establishing RVCA regulations limits to protect additional wetlands

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Full Catchment Report