2003 Progress Report: Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Ecosystem Indicators ComponentEPA Grant Number: R828676C001
Subproject: this is subproject number 001 , established and managed by the Center Director under grant R828676
(EPA does not fund or establish subprojects; EPA awards and manages the overall grant for this center).
Center: Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium
Center Director: Anderson, Susan L.
Title: Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Ecosystem Indicators Component
Investigators: Morgan, Steven , Bennett, Bill , Brooks, Andrew , Gosholz, Ted , Holden, Patricia , Hollibaugh, James T. , Huspeni, Todd , Kendall, Bruce E. , Lafferty, Kevin , Nisbet, Roger M. , Page, Mark , Williams, Susan
Current Investigators: Morgan, Steven , Bennett, Bill , Cherr, Gary N. , Green, Peter , Grosholz, Edwin , Judah, Linda , Kuivila, Katherine , Nelson, Douglas , Nisbet, Roger M. , Smalling, Kelly , Spilseth, Sarah , Vines, Carol , Visinitainer, Tammie
Institution: University of California - Davis , Bodega Marine Laboratory , University of California - Santa Barbara , University of Georgia
Current Institution: University of California - Davis , U.S. Geological Survey , University of California - Santa Barbara
EPA Project Officer: Hiscock, Michael
Project Period: March 1, 2001 through February 28, 2005
Project Period Covered by this Report: March 1, 2002 through February 28, 2003
RFA: Environmental Indicators in the Estuarine Environment Research Program (2000) RFA Text | Recipients Lists
Research Category: Ecological Indicators/Assessment/Restoration , Water , Ecosystems
The overall objective of this research project is to develop a suite of ecological indicators to assess the integrity and sustainability of wetlands in West Coast estuaries rapidly. We propose to develop an integrated suite of indicators to evaluate impacts of stressors across levels of biological organization, trophic structure, life stage, time, and space.
Four approaches were used by teams of investigators from The University of California–Davis and The University of California–Santa Barbara to determine the impacts of stress from nutrient loading, pollution, and exotic species on wetlands from northern and southern California: (1) physiochemical monitoring; (2) biological monitoring; (3) toxicity biomarkers; and (4) statistical analysis and modeling. Research was conducted in concert with the Biogeochemistry and Bioavailability Component (BBC) team to characterize the physiocochemical environment, including temperature, salinity, oxygen, submergence times, sediment grain size, nutrient inputs and toxic contaminant loads; the Biological Responses to Contaminants (BRC) team to conduct toxicity biomarker assays in the field; and the Remote Sensing Component (RSC) team to ground-truth measurements taken at the ecosystem level.
This year, study sites were located at five sites in northern and southern
California, including Walker Creek and Toms Point in Tomales Bay, Stege Marsh
and China Camp in San Francisco Bay, and Carpinteria Marsh. Sites span biogeographic
boundaries, and the estuaries vary morphologically, providing a good test of
the reliability of the indicators to assess wetland integrity across diverse
environments. We: (1) censused the full spectrum of wetland communities, including
microbes, plants, invertebrates, fishes, birds and parasites;
(2) characterized sites for nutrient and toxic contaminants in collaboration with the BRC and BBC teams; and (3) developed modeling approaches that will enable us to determine whether our indicators responded significantly to measured stressors, the ability of indicators to distinguish between reference and impacted sites, and the effects of contaminants on individuals, populations, and ecosystems across space and time. Specifically, indicators are being developed by contrasting conditions at previously characterized reference and impacted sites, following nutrient gradients at all five sites and toxic contaminant gradients at two sites (Stege and Carpinteria).
The development of indicators depends on: (1) the initial establishment of an overarching sampling design that fully integrates the research of each of the five components of the project; (2) the vertical integration of investigations into the effects of contaminants on the wetland ecosystems, beginning with their bioavailability and working up the levels of biological organization from the subcellular to the landscape level; and (3) the development of sophisticated statistical approaches and new models that integrate and make sense of the enormous and diverse array of information that will be obtained during this multifaceted, 4-year project. Because ecosystems subsume lower levels of biological organization, our component has taken the lead, together with the Integration component, to ensure that these three essential criteria are met. We made sure that representatives from all of the research components participated in field sampling, and then we spent a great deal of time discussing the best way to integrate our project based on our initial results and experience. This effort led to the incorporation of a gradient design of contamination at the study sites. The teams returned to field sites to characterize the bioavailability and toxicity of contaminants along the gradient. Invertebrate and fish communities also were characterized along the gradient. A fully integrated sampling scheme was developed and deployed at multiple stations within each of the five sites. Highlights of the preliminary analyses of data for the Ecosystems Indicator Component (EIC) are itemized below. It should be reiterated, however, that all sampling is integrated fully with the other project components.
Dissolved inorganic nitrogen concentration was orders of magnitude greater at Carpinteria than any other site, and it was twice as great at Stege than the rest of the sites. )Δ15N values of macroalgae and selected consumers vary spatially and temporally within the study marshes, and lower crab and snail )Δ15N values at Carpinteria marsh may be related to nutrient inputs from intense agriculture. )Δ15N values appear correlated with salinity suggesting incorporation of land-derived nitrogen in marsh food webs. Nitrogen isotopes may serve as a useful indicator of nutrient enrichment and as a diagnostic tool to assess land-derived sources.
Primary Productivity and Trophic Support
Salicornia, the dominant vegetation of marshes on the West Coast, is smaller, greener, and denser where conditions are saltier and less toxic. In contrast, Salicornia has greater biomass, but more of it consists of brown stems, and plants are less dense where conditions are most toxic.
Spartina was denser, taller, and heavier and had a greater percentage of cover where conditions were less toxic than at our most toxic site (Stege). Furthermore, the percentage of flowering shoots was low at the most toxic site. Mats of cyanobacteria were prevalent at the most toxic sites, unlike at other sites. Ammonification rates, the first step in nutrient recycling, were highest at the most toxic site. Decomposition rates did not appear to be related to toxic exposure.
Linking Plant Stress of Individuals to the Landscape Level
To determine whether the physiological stress of plants can be detected at the landscape level using remote sensing, we calibrated plant physiological performance against known levels of contaminants as a first step to scaling up to the landscape level. Chlorophyll fluorescence and spectroradiometry provide measures of plant physiological performance and health, and can be applied to the landscape level as well as to individual plants. The Normalized Difference Vegetation Index (NDVI) and relative Electron Transport Rate (rETR) at the individual plant level were both sensitive indicators of plant response to cadmium exposure in treatments. Cadmium effects seem to appear first as a decline in NDVI and rETR before a decrease in green biomass. Both parameters could be used as an indicator of plant stress prior to biomass decline, and further experiments are being conducted to confirm these preliminary results.
There were few relationships between vegetation structure and plant tissue cadmium concentrations, and it does not appear that vegetation structure is as sensitive an indicator as the physiological parameters investigated. There appears to be a correlation, however, between above ground biomass and cadmium exposure in Spartina foliosa under controlled conditions, and a similar pattern was found in the field. Cadmium concentrations in Salicornia tissues are higher at a contaminated site (Stege), but biomass and canopy height are lower. Similarly, Salicornia tissue cadmium concentrations were lower at a reference site (China Camp), although biomass and canopy height were higher.
Bacterial diversity differed between polluted and reference sites and is a promising indicator of wetland health. The following results were found: (1) nutrient (DIN) affected bacterial diversity; (2) elevation affected community composition; (3) metals affected bacterial diversity at Stege Marsh; and (4) organic pollutants affected bacterial diversity at Carpinteria Marsh.
Total coliform concentration was correlated with bacterial community composition and urbanization in the Santa Barbara area. Methods that are being developed appeared to detect sources of contamination accurately in laboratory-created “blind” samples. Dog, gull and human sources appear to contain different bacterial communities, and the bacterial community in blind trials appeared to be human in origin. Specifically, bacterial communities varied by host source, diversity increased with size of source, and there appeared to be source-specific peaks. These promising results indicated that terminal restriction fragment length polymorphisms could be a tool in microbial source tracking, but we still need to identify source-specific peaks. This study was coordinated by the Southern California Coastal Water Research Project (SCCWRP), and forges an important collaboration between SCCWRP and the Pacific Estuarine Ecosystem Indicator Research Consortium.
We are determining whether the microfauna in mudsucker digestive tracts collected from contaminant and reference sites differ. If we detect differences, we will determine whether the differences are related to diet (which might reflect a pollutant impact) stress, or other physiological disruptions more directly related to the effects of pollutants.
We are determining whether arsenate reduction could be used as a possible indicator of impacted estuaries. Oxyanions of arsenic, selenium, and other metalloids are cycled actively through microbial communities, where they serve as both electron acceptors and as electron donors for a select group of bacteria. We tested the hypothesis that microbial communities at contaminated and reference sites would differ in the rates at which these oxyanions were metabolized. We found that arsenate is reduced rapidly in all of the sediments we tested, and the reduction rate appeared slowest at a site from a contaminated marsh, Stege. There also were subtle differences in rates that might be detected by shorter incubations with more highly resolved sampling, and the protocol is being refined further.
We are testing whether nitrification would be a potential indicator of impacted estuaries, by comparing ammonia oxidizer populations at various sties. 16S rRNA genes in DNA extracted from sediment samples were amplified with primers NitA and NitB. These amplicons then were used as templates for amplification with GC-clamped variable 3 region, universal primers AM1 and AM2. The amplicons were separated by denaturing gradient gel electrophoresis. Specific ribotypes were shared among sites, and overall patterns were quite variable. We were able to obtain ammonia oxidizer sequences from our samples, and the next step is to compare the results with contaminant load at the different sampling sites.
Ecosystem Condition. Abundance and diversity of infauna appeared to be related to toxic exposure, and results were roughly comparable to those obtained the previous year. Amphipods appeared to be particularly sensitive indicators of stress. Amphipods, especially Corophium, were much less abundant at our most toxic site and may vary with contaminant exposure within Stege and Walker. Interestingly, however, one species of amphipod, Lysanassidae, was far more abundant at our most toxic site, and it was found where contaminant exposure was greatest within the marsh. Contaminant exposure was greater in the marsh, where amphipods were most abundant, than in the channel, which might explain why amphipods were more susceptible to toxic exposure than other infauna.
Potential Indicator of Stress and Reproductive Impairment in Crabs. Field outplants of crabs were conducted at sites along contamination gradients at impacted sites, as well as at reference sites in concert with the BRC team. Preliminary results indicate that crab reproduction may be impaired at impacted sites, and the project is being scaled up for the next field season. For example, females carried smaller broods at a contaminated site (Stege) than at a reference site (Toms Point), indicating that females produced fewer eggs or lost them. In another example, embryos weighed less at the contaminated site than at the reference site, indicating that females invested less energy per offspring, which in turn may affect hatching success and larval survival. Results for nonreproductive crabs, fish, and clams also appear to be promising, and further studies will be conducted this summer.
Potential Indicator of Growth and Reproductive Impairment in Clams. Field experiments were conducted to determine whether growth and reproduction in the clam, Macoma petalum, were linked to biomarkers of stress (stress proteins, lysosome membrane damage, and DNA damage) at different levels of exposure to contaminants. Preliminary data revealed that growth may not differ among the reference and contaminated sites, but it was markedly reduced at one of the stations at the contaminated site. Although the difference in growth was not related to temperature and salinity, it may be caused by different levels of contamination. This has yet to be examined.
Potential Indicator of Ecosystem Function. We determined the link between detrital breakdown, an important ecosystem function, and levels of contaminants to test the hypothesis that the abundance of invertebrate decomposers would be reduced at contaminated sites, thereby slowing decomposition of plant litter. Our initial trial was conducted at a reference marsh and a contaminated marsh in San Francisco Bay. Station M at Stege Marsh, where high levels of soil contaminants occurred, had the slowest rates of decomposition, least richness, and lowest abundance of invertebrate species.
Censuses of Individual Health, Population Size, and Movement. Censuses combined with mark-recapture studies provide valuable population size estimates, movement distances, and important population-wide trends in health (e.g., developmental abnormalities, sex ratios, and disease). For example, fish size shows greater variation at our two most contaminated sites (Stege and Mugu) relative to other sites, and fish livers were larger at contaminated sites than at our reference site at Toms Point.
Growth and Otolith Validation. Efforts to describe accurately the development of Gillichthys mirabilis otoliths continue. Experiments are addressing the periodicity of microstructures and macrostructures, as well as how they relate to somatic growth. Validation of growth rates from otoliths of our model fish species were accomplished and are being used to determine variation in growth rates with toxic exposure.
Ecosystem Studies. Combined with mark-recapture studies, whole ecosystem (community-based) comparisons continue to be made among sites using a variety of taxa.
Data Analysis and Integration. Samples are being processed and analyzed continually. In the coming months, these data will be integrated and used to develop population models that will help us evaluate the health of estuarine ecosystems.
Parasites and Birds
Trematode richness varies with bird richness and may be an effective indicator of community diversity. Trematode frequency and richness are associated with general habitat quality when restoration sites were compared with natural marshes. It also appeared to be greatest at the most contaminated southern site (Mugu), intermediate at Carpinteria, and least in Morro Bay.
Fish ciliates have insufficient spatial variation to be used as indicators at this time and need to be compared with fish toxicology data.
We concluded that our field sites are appropriate, working at them is feasible, and our target species are sufficiently abundant. We detected significant differences in microbial populations between these sites. We have determined that a combination of a gradient design nested within reference and impacted sites is the most powerful design to detect the effects of contaminants on wetland ecosystems. We also concluded that contaminants are likely to be most concentrated in channels and along the margins of tidal creeks, and we are targeting these areas. Additional stations within sites have been incorporated to put the gradient in context to the larger ecosystem. Further discussions of scaling up indicators of plant stress to the level of the landscape using remote sensing revealed that the approach still looks promising. We are developing and validating this indicator in collaboration with the RSC and BBC.
Intensive discussions have been conducted to update our sampling plan for this year. Our plan consists of decreasing intensive broad-scale surveys to enable us to focus on two other priorities. First, we will continue to develop biomarkers during our field outplant experiments. Outplant experiments will be conducted with crabs, fish, and clams at selected stations with sites to measure reproductive and growth performance, biomarker responses, and body burdens in collaboration with the BRC and BBC. Validation and initial field tests of plant stress relative to tissue burdens and bioavailability on the landscape level will continue to be conducted in collaboration with the RSC and BBC. All other promising indicators described above will continue to be developed. Second, we will concentrate on obtaining critical estimates of the population sizes, densities, reproductive seasons, and movements of our three model organisms. These data are needed to link individual measures of fitness to the population level and, ultimately, the ecosystem level. Sampling will be continued at the five sites sampled during this last field season.
After intensive fieldwork is completed this year, integration activities will include the synthesis of indicator data using both multivariate statistics and models. We will draft manuscripts reporting on the potential applicability of individual and aggregate indicators. Working teams will be initiated to formulate recommendations on: (1) plant indicators at multiple spatial scales; (2) indicators for model animals that relate stressor measurements to changes in fitness; and (3) appropriate integrative indicators related to nutrient cycling and bird populations.
Journal Articles on this Report : 1 Displayed | Download in RIS Format
|Other subproject views:||All 32 publications||14 publications in selected types||All 13 journal articles|
|Other center views:||All 139 publications||42 publications in selected types||All 40 journal articles|
||Ward JR, Lafferty KD. The elusive baseline of marine disease: are diseases in ocean ecosystems increasing? PLoS Biology 2004;2(4):542-547.||
Supplemental Keywords:indicators, ecology, estuaries, wetlands, health, toxics, nutrients, exotic species, watersheds, estuary, ecological effects, ecosystem indicators, aquatic, integrated assessment,, RFA, ENVIRONMENTAL MANAGEMENT, Water, ECOSYSTEMS, Ecosystem Protection/Environmental Exposure & Risk, estuarine research, exploratory research environmental biology, Ecosystem/Assessment/Indicators, Ecosystem Protection, Ecological Effects - Environmental Exposure & Risk, Aquatic Ecosystems, Terrestrial Ecosystems, Ecological Monitoring, Ecological Indicators, Risk Assessment, anthropogenic stress, anthropogenic stresses, wetlands, aquatic ecosystem, bioindicator, ecological risk assessment, estuaries, ecosystem assessment, wetland ecosystem, nutrients, bioavailability, trophic effects, ecosystem indicators, coastal ecosystems, environmental indicators, ecosystem restoration, aquatic ecology
Progress and Final Reports:Original Abstract
Main Center Abstract and Reports:R828676 Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium
Subprojects under this Center: (EPA does not fund or establish subprojects; EPA awards and manages the overall grant for this center).
R828676C000 Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Administration and Integration Component
R828676C001 Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Ecosystem Indicators Component
R828676C002 Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Biological Responses to Contaminants Component: Biomarkers of Exposure, Effect, and Reproductive Impairment
R828676C003 Pacific Estuarine Ecosystem Indicator Research (PEEIR) Consortium: Biogeochemistry and Bioavailability Component