Natural Resources Monitoring Program

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Natural Resources Monitoring Program CHANNEL ISLANDS NATIONAL PARK NATURAL RESOURCES MONITORING PROGRAM 1990 STATUS REPORT Prepared by: Gary E. Davis Research Marine Biologist and William L Halvorson Research Biologist National Park Service Cooperative Parks Study Unit University of California, Davis December 15, 1990 Channel Islands National Park TABLE OF CONTENTS Summary 1 Introduction 1 Project Description 1. Objectives 3 2. Methods 4 3. Costs of Major Tasks 12 Project Productivity 1. Degree of Completion 14 2. Products 14 Plans for Continued Monitoring 18 Servicewide Applicability 18 Literature Cited 19 Tables 1. List of monitoring protocol handbooks 7 2. Summary of population parameters monitored 8 3. List of design studies, with costs, funding sources, & years ... 13 4. Publications from the project 15 6. Summary of monitoring handbook distribution 17 Figures 1. Map of Channel Islands National Park and vicinity 2 2. Step-down plan for natural resources monitoring at Channel Islands National Park, California 6 3. Budget for implementing the designed natural resources monitoring program at Channel Islands National Park .... 22 i Natural Resources Monitoring Program: Status Report Summary A system for monitoring population dynamics of index taxa was developed to define and evaluate ecosystem health in Channel Islands National Park. A Delphi technique with rating criteria was used to select potential index taxa. Nearly 500 species of the 2,000 known from the park were tested for long-term monitoring. Most of the index species are insects (200) or terrestrial plants (156). The remainder are marine invertebrates (41), birds (23), marine algae (16), fishes (15), and mammals and herptiles (12). Population parameters monitored include abundance, age structure, reproductive effort, recruitment, growth rate, mortality rate, and phenology. A local area network (LAN) of microcomputers and a geographic information system (GIS) were established to manage the monitoring 'data. Monitoring protocols were documented in a series of published handbooks and distributed widely as a prototype program. Introduction Channel Islands National Park, created in 1980, is comprised of five islands and over 50,000 ha of coastal waters in the southern California bight (Figure 1). The islands range in size from tiny 260 ha Santa Barbara to the giant 25,000 ha Santa Cruz. The islands support some of the last examples of natural Mediterranean ecosystems in North America. Forests of endemic Santa Cruz Island pine (Pinus remorata), and the rare Torrey pine (P. torreyana), and groves of endemic island oaks (Quercus tomentella), fern-leafed Catalina ironwood (Lyonothamnus floribundus), and Catalina cherry (Prunus lyonii) are interspersed with extensive grasslands and coastal sage communities on the larger islands. The park contains much of what remains of the natural coastal ecosystems of southern California, including a coastal marsh on Santa Rosa and exceptionally pristine tide pools that occupy extensive marine terraces surrounding all of the islands. Prime examples of the northern hemisphere's giant kelp forests (Macrocystispyrifera) are found in the park's coastal waters. The richness of the park's marine environment is further reflected by some of the largest and most diverse sea bird and pinniped rookeries in the world. The park lies on the boundary of two major biogeographical provinces. This boundary is particularly noticeable in the marine environment (Murray et al. 1980, Seapy and Littler 1980). The western-most islands of San Miguel and Santa Rosa are bathed by cold northern waters of the boreal Oregonian province carried south by the California current. Waters surrounding the southeastern islands of Santa Barbara and Anacapa come from the south along the mainland coast and support a warm temperate biota known as the Californian province. Santa Cruz Island sits directly astride this boundary, where plants and animals from both provinces mingle and create a unique assemblage of species capable of adapting to the variable conditions of the transition zone. Park waters harbor biota representative of over 1,600 km (1,000 mi) of the North American coast from Ensenada, Mexico, to San Francisco, California. 1 Channel Islands National Park Prevailing winds and the bathymetry of adjacent basins also greatly influence biological communities in the park. Winter storms bring rain and buffet the islands' northern shores, whereas biota of the southern coasts reflect a dryer, more sheltered environment. The confluence of major oceanic currents and the shape of the continental shelf create a rare phenomenon of persistent upwelling near the park. Nutrient-rich water wells up from the deep sea near Pt. Conception, on the mainland coast to the north, and produces exceptionally productive food webs in the waters around San Miguel and Santa Rosa Islands (Parrish et al. 1981, Dayton and Tegner 1984). 2 Natural Resources Monitoring Program: Status Report Many of the park's exceptional values are a product of isolation from mainland populations. A million years of physical isolation from mainland ecosystems allowed island forms to evolve independently (Vedder and Howell 1980). Physical difficulty of travel to and from the islands protects them even now. Benefits of isolation are particularly apparent with respect to sea birds and marine mammals that once bred in many areas of the mainland coast; today they find sufficient freedom from civilization and human disturbance only on the offshore islands. Channel Islands National Park exists on the edge of a human tide. Nearly 15 million people reside on the adjacent mainland coast. As visitors to the park, these neighbors seek solitude, recreation, and knowledge of their environment, but bring with them threats of crowding, trampling, and .disturbance of fragile and extremely limited island and marine habitats. Air quality in the nearby Los Angeles basin is among the worst on Earth, exceeding federal ozone standards of 120 ppb more than 100 days a year. Strong seasonal easterly Santa Ana winds carry the polluted air offshore into the park (ozone levels on Anacapa Island exceed 200 ppb during these events) threatening sensitive plant communities like the rare Torrey pine forest on Santa Rosa Island. Nearshore currents carry urban runoff and wastewater effluent northwesterly from the metropolitan centers of Los Angeles and Orange counties into park waters. Major offshore petroleum exploration and development in the adjacent Santa Barbara Channel and up-current and up-wind in the nearby Santa Maria Basin brings with it the potential of additional air and water pollution. State managed fishery harvests in the park remove 4,500 to 6,800 tonnes of giant kelp, rock fish, halibut, angel shark, sea urchin, lobster, abalone, and dozens of other fish and shellfish each year. This biomass constitutes about 15% of California's total nearshore harvest, yet the park contains only 3% of the state's coastal waters. This selective removal of target species threatens the stability and integrity of park ecosystems. Hunting and land use practices on the islands have also taken their toll over the past 250 years. Fur hunters virtually eliminated sea otters and drastically reduced seal and sea lion populations in the 18th and 19th centuries. Ranching and farming on the islands in the 19th and 20th centuries introduced alien plants and animals that out-compete, eat, and replace rare endemic natives (Halvorson, et al. 1988, Clark, et al. 1990). Project Description OBJECTIVES While the park still harbors spectacular wildlife displays and inspires awe, past environmental insults and continued human impacts require active intervention and management to restore and protect basic park values. Restoration and protection of park resources requires an ecological monitoring program to assess the effectiveness of these efforts, and to determine limits of natural variation, diagnose abnormal conditions, and prescribe potential remedial treatments. The objective of this project is to provide that ecological monitoring program. 3 Channel Islands National Park Just as a physician monitors a patient's vital signs, natural resource managers need to be able to monitor an ecosystem's vital signs. There are several ways to monitor ecosystem health. Measures of energy flux, biodiversity, constituent budgets, and population dynamics are among the most well-developed (Orians 1986, Conant et al. 1983, Odum 1959). The population dynamics approach best meets National Park Service management requirements to: • accurately reflect ecosystem conditions, • provide easily interpreted results, • project future resource conditions, • use readily available sampling techniques, and • provide information directly applicable to management issues. Population dynamics of selected species also offer relatively unambiguous insights to ecosystem structure and function. Organisms integrate the effects of a vast array of ecological factors, including predation, competition, and environmental conditions that are expressed as changes in readily measured population parameters such as abundance, distribution, and growth and mortality rates. Measures of population age structure, reproductive efforts, and recruitment provide glimpses of the future and early warnings that remedial management actions are needed. METHODS A conceptual model of park ecosystems was used to identify 15 mutually exclusive system components that scientists are trained to study at the population level, such as pinnipeds, sea birds, terrestrial plants, and
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