Incorrect for the last 30 years? Evidence for updated boating capacity standards on lakes and reservoirs. Jeffrey Hallo Geoffrey Riungu Jessica Fefer

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Incorrect for the last 30 years? Evidence for updated boating capacity standards on lakes and reservoirs Jeffrey Hallo Geoffrey Riungu Jessica Fefer

Acknowledgments This project was conducted under contract and in collaboration with Grant County Public Utility District Special thanks to the following people: Brad Harshman Jerri Mickle Shannon Lowery Garret Stone Devyani Singh Sarah Wilcer Emma Pappas

Introduction Recreational boating is one of the major water-based recreation activities (Mahoney & Stynes, 1995; USCG, 2014). 35.7% of the U.S. adult population 87.3 million Americans participated in recreational boating at least once in 2014 (NMMA, 2015). U.S. expenditures on boats, engines, accessories, and related costs totaled $35.4 billion in 2014 (NMMA, 2015).

Introduction Recreational boaters enjoy a multitude of public natural lakes. Reservoirs associated with hydropower dams have greatly expanded these opportunities, providing boating for millions of Americans. Carrying capacity is a perennial issue on lakes and reservoirs because: Boating use levels are high Boating is concentrated seasonally Boating safety is a substantial concern Recreational enjoyment is influenced Regulatory or planning requirement (e.g., FERC Form 80, relicensing)

Carrying Capacity - Conceptual Diagram Carrying Capacity Physical Managerial Fundamental More objective and less complex Compare use to existing space (e.g., facility design standards) and organizational capabilities Adapted from Manning (2010)

Resource-based Carrying Capacity

Experiential Carrying Capacity

Carrying Capacity - Conceptual Diagram Experiential Resource Carrying Capacity Physical Managerial More subjective Inherent connection with recreation mission and conservation objectives Adapted from Manning (2010)

Planning Frameworks: A Means to Address Carrying Capacity Primary frameworks used in recreation management: Limits of Acceptable Change (LAC) Visitor Experience and Resource Protection (VERP) Interagency Visitor Use Management Council Framework These frameworks all have a common rationale and procedure: Formulate management objectives and associated indicators and thresholds (i.e., standards) Monitor indicator variables Apply management practices to ensure that standards are maintained

Indicators Indicators are defined as measurable, manageable variables that reflect the essence or meaning of management objectives Indicators often represent what is most important about the resources or the visitor experience (or both). Example: Number of encounters with other boats per day

Thresholds Minimum acceptable condition of an indicator Example: A person should encounter, on average, no more than 10 other boats per day Norms may be used as the basis for thresholds Commonly accepted beliefs about what behavior or conditions should be Defensible because they are based on public input Often context-specific May be formulated using a social norm curve

Acceptability Social Norm Curve 4 Optimal or Preferred Condition 3 2 1 0 Range of Acceptable Conditions Minimum Acceptable Condition -1-2 -3-4 0 2 4 6 8 10 12 14 16 18 20 Number of Boats Encountered Per Day

Recreational Carrying Capacity Defined Recreational carrying capacity is the point at which impacts from visitor use violate a threshold In our hypothetical example from previous slides, recreational carrying capacity is reached once a person encounters, on average, more than 10 other boats per day

Benefits of this Approach Useful for both experiential and resource impacts Stakeholder-driven, science-based, and well-tested Objective and based on empirical data it is a public input process Decisions made using these frameworks are documented, supported, and defensible These frameworks are well-accepted and broadly used

Boating Capacity Thresholds Determinations of lake and reservoir boating carrying capacity often focus on boat density as a key indicator Boat density thresholds are often expressed as acres of surface water per boat Thresholds for boating density: Vary widely in the published literature Are in many cases from sources that may be out of date some are more than 30 years old Are context specific and may not be generalizable In some cases seem to lack empirical evidence

Source National Recreation and Parks Association Bureau of Outdoor Recreation Arizona Outdoor Recreation Coordinating Commission Wisconsin Comprehensive Plan Louisiana Parks and Recreation Commission Cascade Reservoir Resource Management Plan Suggested Boat capacity 4 acres/boat 3-18 acres/boat 10-20 acres/boat 20 acres/boat 20 acres/boat 25 acres/boat Bureau of Reclamation (2011) (for suburban and rural developed waters) (for Rural Natural) 1-3,200 acres/boat 10-50 acres/boat 50-110 acres/boat Warren and Rea (1989) EDAW Inc (2000) 1.3-12 acres/boat 15-20 acres/boat **Sources if not marked above: NRPA (1981); EDAW (1981, 1990); BOR, USDI (1970); URDC (1977)**

Project Rationale and Objective Boaters' perceptions of crowding have seldom been used to determine recreational boating thresholds (Tseng et al., 2009). This is despite the fact that overcrowding of recreational boats can affect the well-being and safety of visitors Crowding and safety are strongly connected to people s perceptions Objective: Develop updated and context-specific thresholds for motor boating density at two reservoirs based on boaters perceptions and normative methods.

Study Area: Priest Rapids and Wanapum Reservoirs

Visitor surveys conducted in Summer 2015 (n=656 on Wanapum, 92 on Priest Rapids) Motor boaters (n=170 on Wanapum, 21 on Priest Rapids) were asked to evaluate six photos that showed a range of boat crowding on the lake Evaluations were on three scales acceptability, management action, and typically seen Photos were developed to balance and help prevent bias from these factors: Placement (to emphasize density versus interactions) Type of motorboat Methods Foreground versus background Movement (under power versus not under power)

27.4 surface acres of water per boat

13.7 surface acres of water per boat

9.1 surface acres of water per boat

6.9 surface acres of water per boat

4.6 surface acres of water per boat

3.4 surface acres of water per boat

Motor boaters were asked: We would like to know how many boats you think could use the segments of the reservoirs that you used today without you feeling too crowded and unsafe. To help judge this, we have a series of photos that show different numbers of boats. Please look at these photos. Please rate each photo by indicating how acceptable you think it is based on the number of boats shown. A rating of -4 means the number of boats is very unacceptable, and a rating of +4 means the number of boats is very acceptable.

Results - Wanapum

Results Priest Rapids

Results In the same survey, motor boaters were asked: Which photo shows the highest number of boats that should be allowed on the reservoir segments you used today? In other words, at what point should boats be restricted from using the reservoir because it is too crowded and unsafe? Priest Rapids Reservoir Wanapum Reservoir Mean Photo (acres/boat) SD None of the photos show a high enough number of boats to restrict use 4.0 (9.1) 1.5 58.8% 4.8 (5.1) 1.4 68.2%

Results In the same survey, motor boaters were asked: Which photo looks most like the number of boats you typically saw on the reservoir segments you used today? Mean Photo (acres/boat) SD Priest Rapids Reservoir 2.4 (11.9) 1.4 Wanapum Reservoir 3.9 (7.1) 1.8

Conclusions 3 acres/per boat is acceptable to boaters on both reservoirs. 7 acres/boat was reported, on average, as the maximum boat density before use should be restricted, but A majority of survey respondents felt that boating use should not be restricted even when boat densities are greater than 3 acres per boat Results suggest that a boating capacity threshold of 15 to 20 surface acres of water per boat as previously applied to the reservoirs (EDAW, 2000) is unsupported by empirical data and too restrictive.

Conclusions A threshold of 5 acres per boat is recommended and applied in the boating capacity determinations Boaters typically experienced 11.9 and 7.1 acres/boat on the Priest Rapids and Wanapum Reservoirs By comparing these with a threshold of 5 acres per boat, it suggests that the Priest Rapids and Wanapum Reservoirs are utilized for boating, on average, at 42.2% and 70.4% of their capacity, respectively.

Conclusions Other indicators may be important launch waiting times and % parking used at boat launches At both study reservoirs boating capacity was 12.5% and 33.3% based on these indicators

Future research should examine boat speed and proximity as potential indicators Need to use boating thresholds that are: Updated Take into account context and boaters perceptions Based on empirical data Conclusions Use methods that are rigorous and defensible Where possible, use normative methods to develop place-based boating capacity thresholds Accurate boating thresholds are critical because they serve as the basis for many decisions related to recreational access, facilities, and related management.

Questions and Discussion Dr. Jeffrey C. Hallo Parks, Recreation, &Tourism Management Clemson University jhallo@clemson.edu ; (864) 656-3237