ࡱ> rtq@ j:bjbjFF (r,,0$$$$L$z4%%%%%%%%4444444f5R74*%%**4%%44f,f,f,*j%%4f,*4f,f,.-/%z% @/L$"+X.1J40z4/,~8z+~8-/-/~8/%H&f,'t(D%%%44$J,Summary: Maine Lake Classification, Condition Assessment, and Initial Portfolio Prioritization Prepared by Arlene Olivero 2/28/2006. Edits Josh Royte and Kathy Jensen 3/11/2006 and Barbara Vickery Edits as of 3/27/2006 GIS Based Classification All lakes in Maine were tagged with a number of geographic and morphologic variables. These variables included size, elevation, shoreline complexity, depth, connectivity to stream networks, buffer wetland cover, and the presumed buffering capacity of the lake waters based on the geology of the watershed and a buffer zone. Of these variables, five primary variables (size, elevation, depth, stream connectivity, and buffering capacity) were thought to be most highly correlated with lake ecosystem types in Maine. These five variables were chosen based on expert review (P. Vaux, K. Webster, L. Bacon, D. Courtemanch, A. Olivero) and were combined to form a simplified GIS based lake classification to stratify the diversity of lake ecosystem types for representation in TNC conservation planning efforts. The 10,349 lakes and ponds in Maine fell into 105 unique types when their values in the classes of these 5 primary variables were combined. For example, the most common lake type was 1-9.99 acres, < 800ft in elevation, < 30 ft deep, of medium-high acid neutralizing capacity, and connected to streams. Similarly, the most common lake type in the next size class, 10-100 acres, was < 800ft in elevation, < 30 ft deep, of medium-high acid neutralizing capacity, and connected to streams. Half of the 105 lake types have fewer than 10 examples and 23 types have only one example in that type. For further information on the lake classification please see the Maine Aquatic Biodiversity report, the lake classification PowerPoint presentation on the resource CD, and the full lake classification tables and reports within MEAquaticsdata_20060303.mdb (located in I:\Ecoregions\Final_Plan_CDs\NAP_cd\tabular\aquatics\Appendix6_Expert&StateReview\me) Simplified Classification Based on 5 Primary Variables: Combined to form 5 digit lake type code (RC_SEDNC)SIZECLASSacre class 10000= 0-.99, 20000= 1-9.99, 30000= 10-99.99, 40000= 100-999.99, 50000= 1000+ELEVCLASSelevation zone of the lake 1000= 0-800ft, 2000 = 800-1700ft, 3000 = 1700-2500ft, 4000= 2500+ftDEPTHCLASS100 if >= 30ft, 0 if < 30ft, if no survey assume < 30ftNORTRCReclass of Dominant Norton class in the DDV or 12 digit watershed of lake; 10=Low to no acid-neutralizing capacity, 20=Medium to High acid-neutralizing capacity, 40="Infinite" acid-neutralizing MAX_D100C1 = connected to stream, 0 = unconnected to stream  Lake Condition and Biodiversity Value Screening A large number of attributes were assigned to each lake to facilitate assessing their current condition and biodiversity value. When building a comprehensive and representative portfolio for conservation it is more efficient to select lakes already in good condition when there are enough of that lake type to select from. Current condition was assessed using primarily GIS sampled variables related to the land cover, roads, dams, and population near the lake. Biodiversity value was assessed based on additional attributes related to the presence of primary conservation targets such as rare aquatic dependant species or aquatic natural communities, outstanding fisheries, wild brook trout, wild lake trout, % native fish, and fishless lakes. Indicators of impacts to native biodiversity were also used to assess the current condition and biodiversity value, such as identifying lakes where there was a stocking history. A series of expert review meetings were also held to gather expert comments on each lake to incorporate expert knowledge about the condition and biodiversity value of the lakes. Please see the TNC Maine aquatics database MEAquaticsdata_20060303.mdb (located on the Resource CD\NAP_cd\tabular\aquatics\Appendix6_Expert&StateReview\me) for an entire list and description of the condition attributes, biodiversity attributes, and expert comments. Numeric Goals for Portfolio Inclusion Minimum goals for numbers of lakes to include in the portfolio were set for each lake size class. Given the large number of lakes that are <10 acres in size, the team decided to focus the portfolio review on lakes >=10 acres (2,716). Goals for the number of lakes to include in the portfolio were guided by goal numbers used in standard TNC Ecoregional Planning Goals for Species and Communities in the Eastern Region to ensure adequate replication of conservation targets in the portfolio. Minimum Goals based on Lake Size Size 5 lakes, > 1000 acres10 examples of each lake type (RC_SEDNC)Size 4 lakes, 100-999.99 acres, 4000020 examples of each lake type (RC_SEDNC)Size 3 lakes, 10-99.99 acres, 3000040 examples of each lake type (RC_SEDNC) We did not specifically set higher goals for rarer lake types but, because the Size 4 and 5 lakes are less common, a higher percentage of them will be represented using the above goals. When the goal for a lake type was more then met by a large number of that type protected in within conservation land, then more were accepted into the portfolio. Distribution Goals for Portfolio Inclusion: Stratification across HUC10 Watershed System Types In conservation planning, it is important not only include replicate examples of conservation targets in our portfolio but to also represent those targets across the larger geographic range of settings upon which they occur. To address these geographic distribution issues, we picked the best lakes within a type and then checked to see how those were distributed across HUC10 watershed system types. Where distribution was uneven (e.g. when most were in one HUC10 type), we then looked at the lake examples in this lake type more carefully to determine if viable examples existing in other HUC10 types could be found. Although there were 13 original HUC10 system types defined in Maine, the types were collapsed into 6 major types to simplify our distribution review (1 = types 9, 10, or 11; 2 = types 7 or 12; 3 = types 8 or 13; 4 = types 3 , 5, or 6; 5 = types 1 or 4; and 6 = type 2) Portfolio Codes The following portfolio priority codes were assigned to the lakes: EOLake has a notable element occurrence, but the entire lake is not portfolio-worthyL1Best examples of lake type.L1bNot in as good condition as L1, use if need more lakes to meet goals.L2Not good enough to select, but meets basic condition criteria.NSNot selected. Lakes with no portfolio code were lakes that did not stand out as good or poor quality and were not specifically discussed. Portfolio Assembly A small team of local experts and TNC staff held a series of meetings to select portfolio lakes based on the above goals and review of the collected classification, condition, biodiversity value, and expert comments. For this meeting, condition and biodiversity attributes were summarized to help the divide lakes into four categories qualifies for automatic team review based on high priority attributes qualifies for team review based on other priority screening criteria meets top landscape context condition criteria, and meets top conservation land protection criteria. Lakes were also noted as suggested for dropping from review if their EPA 305b impact or dam impact class was too poor. Fields used in prioritizing lakes for portfolio reviewAUTO_PORT1 = within 100m of S1 river, 2 = within 100m of S2 river, 3 = within 100m of Sx river, and 4 = surrounded by or part of any Viable Ecoregional Target Natural Community (all 1st iteration Portfolio = Y and new EORANK A or B communities), regardless of size, excluding Matrix blocks where size of Element Occurrence is 50 or greater than size of the lakeAUTO_SPCFSpecial Lakes that have the following: 1 = Wild Brook Trout, 2 = Wild Lake Trout; 3 = primary target mussels, 4 = any of MNAPs rare lake plant Element Occurrences, 5 = are a fishless lake (are about 24 of these), 6 = high elevation (>2500, are about 20 of these), 7 = have Blueback trout or Char (primary target fish Element Occurrences), 8 = have Dwarf Whitefish, 9 = other primary aquatic Element Occurrence within 300m (turtle, sedge, dragonfly)AUTO_RARERarity: 1= Any lakes of size 50000 for which there are fewer than 10, or of size 40000 for which there are fewer than 20, or of size 30000 for which there are fewer than 40 statewide 2 = there are <= 2 per system type, or 5 = there are <= 5 per HUC10 13 type stratificationSCR_BIOFGScreening Biology Flag: 1 = Aquatic Experts nomination as benchmark or unique/critical area; 2 = Never stocked; 3 = 100% native fish species SCR_REMOTEScreening Remote: 1 = no class 1-6 roads within 500m, 2 = LURC zoned remote, 3 = LURC zoned remote and no roads within 500m SCR_STR1Screening: within chosen Size 2 Port STr1 watershedSCR_100T1Screening: 95% lake buffer is within Tier 1 MatrixTOPLCSUMTop 1st or 2nd tenth-ile in Buffer and Watershed Land cover in either in 5 digit lake type code, in size class, in 5 digit code stratified by HUC10 watershed system type RC_SEDNC = 100, SZ =10, HUCTY = 1; Null means not in top 1 or 2 quartiles?TOPG123Both watershed and buffer GAP123 >= 50% and not in DROP category DRP_305BScreening: 305b category 3-5 (Category 3 - 303d watch list lakes)DRP_DAM23Screening: Dam category 2 or 3 (ranking of 1, 2, 3, dam impact from MDIFW; 2 and 3 are considered impacted. 1=no functional dam; 2= >50% man-made flowage; 3= <50% man-made flowage. 0=in IFW database but no data available. Null=not surveyed)  Results Of 2,716 lakes evaluated (i.e. all those >+ 10 acres) 659 were recommended for inclusion in the portfolio as the highest qualifying class of L1. Please see the TNC Maine aquatics database MEAquaticsdata_20060303.mdb (located on the Resource CD\NAP_cd\tabular\aquatics\Appendix6_Expert&StateReview\me) for an entire list of portfolio lakes and reports on their attributes. Representation: The project classified 105 distinct types of lakes; 54 types for lakes at least 10 acres in size. The portfolio included representation of 51 of those types. Types not selected include lakes that are flowages and some other lakes that did not meet screening criteria for condition or biodiversity value, however they could be considered for inclusion if there is adequate evidence of unique ecosystems. Protection: Over 950 lakes in Maine have more than 95% of a 200 meter buffer around them in some level of conservation protection. Most of these are small, only 154 are 10 acres or great in size. Of those lakes with mostly protected buffers, 72 were selected for the portfolio. However if you look at a higher level of protection, reserve-level protection of the 200 meter buffer, then only 27 of the 10 acre or larger lakes are protected and the portfolio includes all but two of those. Natural Cover in Buffers: Over half of the ponds in the state have predominantly (>95%) natural cover in the 1000 meter buffer surrounding them. This is also true of just the larger ponds that were looked at for the portfolio. Seventy-five percent of the ponds selected for the portfolio (493 of them) also meet this natural cover threshold. Remote Ponds: Ponds with no known roads within 500 meters of their shoreline are thought to be at a lower risk of over-fishing, invasives introductions, and impacts from both roads and development. Over 1,600 lakes in the state meet this standard, but only 132 Great Ponds (those equal or greater to 10-acres) do. The portfolio includes 44 of these. Fisheries: Only 5% (591) of the states ponds are documented to have 100% native fish and most of those (517) are the larger ponds we screened. This suggests that ponds under 10 acres are simply not sampled well. There are also 61 ponds that were documented as still fishless, although all but 9 of those are less than 10 acres in size. Invasives: Twenty one of the states lakes have documented infestations of invasive plants. None of these are less than 10 acres (sampling effort again?). Water Pollution: Sixty-seven lakes in Maine are listed as watch list waters by the state because they do not meet attainment goals for water quality standards. They are all larger lakes. Three of these were selected for the portfolio because of their importance for biodiversity values that are not yet noticeably impacted by water quality.  Watersheds were classified into system types based on similar amounts of bedrock and surficial geology types, landform types, and elevation zones in the 10-digit HUC watersheds.  River ratings were S1 for top priority in excellent condition; S2 priority in moderate condition, but needed for representation; and Sx for selected because important for connecting, but in poor condition.  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