Merritt TSR Data Package - 2014 FRPA Section 8(8) (x)(x) GAR Section 15 – Temperature Sensitive Streams FPPR Section 53 – Temperature Sensitive Streams Factor xx – Temperature Sensitive Streams Christian St-Pierre Part 1 Factor Description Description: Stream temperature conditions are critical for fish, and temperature shifts associated with climate change are predicted to be an important factor in various physical and biological watershed processes (Pike et al. 2010a). It is envisioned that, by implementing existing and proposed regulations that help mitigate stream temperature sensitivity and by ensuring that appropriate management strategies are used at the operational level, maintaining riparian thermal buffering functions will help mitigate the predicted impacts of climate change. In British Columbia, riparian areas are protected from adverse effects of forest harvesting by applying mandatory no-harvest reserves to all fish-bearing streams > 1.5 m wide. However, there is no regulatory requirement for riparian reserves on small fish-bearing streams (< 1.5 m channel width) and on all non-fish-bearing streams regardless of channel width. Section 15 of the B.C. Government Action Regulations (GAR) 1 provides for the use a regulatory tool that allows forest managers to designate “Temperature Sensitive Streams” (TSS) to protect critical fish-bearing streams that could be altered by stream heating. A TSS designation applies to all riparian class but particularly to S4, S5, or S6 streams2 which, by definition, do not have mandatory riparian reserves under the Forest and Range Practices Act. Section 53 of the Forest Planning and Practices Regulation enhance protection by stipulating: An authorized person who fells, modifies or removes trees in a riparian management area adjacent to a temperature sensitive stream, or a stream that is a direct tributary to a temperature sensitive stream, must retain either or both of the following in an amount sufficient to prevent the temperature of the temperature sensitive stream from increasing to an extent that would have a material adverse impact on fish: (a) streamside trees whose crowns provide shade to the stream; (b) understory vegetation that provides shade to the stream. Forest and Range Practices Act – Government Actions Regulation – Temperature Sensitive Streams. Available at: http://www.qp.gov.bc.ca/statreg/reg/F/ForRangPrac/582_2004.htm#section15 1 2 S4 = fish-bearing streams (< 1.5 m wide); S5 = non-fish-bearing streams (> 3 m wide); S6 = non-fish bearing streams (< 3 m wide) Merritt TSR Data Package - 2014 Spatial extent of stream network requiring management (Excerpt from Reese-Hansen 2012) Section 53 of the FPPR requires the following practice: “An authorized person…must retain…[riparian vegetation] sufficient to prevent the temperature of the temperature sensitive stream from increasing to an extent that would have a material adverse impact on fish”. To determine the spatial extent of the protection several key definitions described in the FPPR, and that apply to both the GAR and FPPR, must be understood. The first is “fish stream” as used in the GAR. The FPPR defines a fish stream in one of two ways; a watercourse that: “(a) is frequented by any of the following species of fish: (i) anadromous salmonids; (ii) rainbow trout, cutthroat trout, brown trout, bull trout, Dolly Varden char, lake trout, brook trout, kokanee, largemouth bass, smallmouth bass, mountain whitefish, lake whitefish, arctic grayling, burbot, white sturgeon, black crappie, yellow perch, walleye or northern pike; (iii) a species identified as a species at risk; (iv) a species identified as regionally important wildlife, or (b) has a slope gradient of less than 20%, unless the watercourse (i) does not contain any of the species of fish referred to in paragraph (a), (ii) is located upstream of a barrier to fish passage and all reaches upstream of the barrier are simultaneously dry at any time during the year, or is located upstream of a barrier to fish passage and no perennial fish habitat exists upstream of the barrier”. Therefore, the spatial extent of the designation is first defined in GAR (s.15) by both, the known distribution of fish, or the physical parameters that restrict the movement of fish throughout a stream network. The FPPR classifies fish streams as one of four possible stream classes (S1, S2, S3, or S4) and, by way of the GAR designation, requires retention of stream side vegetation. Because the FPPR clearly requires riparian retention on all S1 through S3 streams, regardless of the stream’s temperature sensitivity, these streams receive riparian buffering by default. However, the GAR extends this buffering requirement to S4 streams. Like an S4 stream, normally, the remaining stream classes (S5 and S6) do not necessarily require streamside vegetation retention as the option is provided to a Forest Act agreement holder to retain an amount along these streams between 0% and 100%. Under TSS management requirements however, it is along S5 and S6 streams that the practice requirements are also increased (see Table 9). The FPPR (section 53) does this by additionally requiring forest management activities to retain stream side Merritt TSR Data Package - 2014 vegetation along “direct tributary” streams to a TSS (i.e. a S1 to S4 stream). To understand how this would be translated to the stream network the term direct tributary requires examination. The FPPR defines this term as a portion of a tributary stream that: “(a) is a minimum of 100 m in length, and (b) has the same stream order as the most downstream reach of the tributary” In this way, the spatial distribution of the stream network is limited to fish streams and direct tributaries and accordingly in many cases headwater streams will be omitted. Table 9 helps describe the interpretation of the TSS stream-network using the FPPR defined term “direct tributary”. Figures 7 illustrates the application of GAR s.15 and the FPPR s.53 to a stream network. Note that in all examples below, if the direct tributary were less than 100m long, it would not require any additional management. Table 9. FPPR base-case riparian management versus TSS management (From Reese-Hansen 2012) Merritt TSR Data Package - 2014 Figure 7. Application of GAR s.15 and the FPPR s.53 to three different stream networks in three similar sized watersheds (From Reese-Hansen 2012) TSS Gross land base (ha) Nicola Watershed 780 000 Other Details: Won’t be part of base case but will be a binder factor, as decision has not been made to approve TSS GAR Order at time of data package. Do a sensitivity based on the modelling instructions below. Andrew to assist with developing the sensitivity. How Modelled: The FPPR s.47 – Stream riparian classes, stipulate the minimum riparian management width, riparian reserve zone width and riparian management zone width on each side of the stream. Within the Nicola watershed boundary and where FRPA applies, every fish bearing streams (S1-S4) and every direct tributary (S5-S6) to a fish bearing stream will be buffered to the Riparian Management Area width. Merritt TSR Data Package - 2014 Sources: Contacts: Christian St-Pierre, Ecosystems Section, MFLNRO, Kamloops. christian.stpierre@gov.bc.ca Lars Reese-Hansen, Watershed/Ecosystems Planning Biologist, MFLNRO, Victoria. Lars.ReeseHansen@gov.bc.ca Alison Peatt, Biologist, Bearfoot Resources Ltd, bearfootresources@shaw.ca Author: Christian St-Pierre, Ecosystems Section, MFLNRO, Kamloops. christian.stpierre@gov.bc.ca References: Reese-Hansen, Lars, Marc Nelitz, and Eric Parkinson. 2012. Designating Temperature Sensitive Streams (TSS) in British Columbia: a discussion paper exploring the science, policy and climate change considerations associated with a TSS designation procedure. Ministry of Environment, Fisheries Management Report RD# 123. Victoria, BC. 71pp. Status: Assessment of the conservation value, completed April 2013 Update Date: April 8, 2014 Appendices: Part 2 - Data Set Description (part 2 may not be needed for each factor) Description Source File Metadata: Currency Date: Primary Fields of Interest: TSA summary of data set: Author: Update Date: File Tracking: Merritt TSR Data Package - 2014 Appendices: