Wetland ecology is a complex subject that draws
from several scientific disciplines. While classroom lectures are
necessary to teach the vast body of scientific data, there is no
substitute for field and laboratory experiences to enrich learning. This
paper describes methods for teaching a wetland ecology class based
mainly on direct, hands-on field experiences for students.
“Help! I have to teach wetland ecology! What are you
doing?” I was no stranger to this plea, having made it myself to
colleagues years earlier. When I accepted a position teaching wetland
ecology at the University of Maryland, I contacted people I knew who
were leading similar courses, incorporated field and laboratory
techniques that I had used in graduate school, and researched new
methods to fill in the gaps. Many more techniques are available,
however, than can be used in a semester-long course. The difficulty
comes in selecting activities that students will like, finding the time
and facilities needed, and determining the types and proximity of
wetlands.
Courses in environmental biology or ecology lend
themselves naturally to exciting outdoor experiences (e.g., Grove 1984;
Stephens et al. 1988). Many of the field trips described in the
literature, however, are travel-study courses lasting from a week to a
month (Grove 1984; Lopushinsky and Besaw 1986; Stephens et al. 1988;
Ferrier 1989). Only a few papers discuss how to incorporate field and
laboratory exercises into semester-length ecology classes (Gill and
Burke 1999; Cahoon 1996; Switzer 1995), possibly because of the
difficulties of developing and implementing effective field exercises
for a three-to-four-hour lab period.
Despite the wealth of possibilities for interesting
activities in wetland ecology specifically, I have only found articles
that describe using wetlands to teach ecology at a community college (O’Neal
1995) and others on wetlands as outdoor classrooms for primary and
secondary school education (e.g., Texley 1988; Kerr 1996; Stewart 1998).
In one interesting and effective module of an undergraduate ecosystem
ecology class, students evaluated quantitative data from journal
articles related to wetland biogeochemistry to see how the data
corresponded to criteria for wetland delineation (Camill 2000). While
this class did incorporate a lab, the focus of the paper was on a
wetland biogeochemistry case study, which did not involve student field
or lab work.
Wetland ecology is an increasingly popular course
offering in the United States and elsewhere (a list of colleges and
universities offering courses or programs in wetland science or ecology
can be found on the Society of Wetland Scientists’ website at http://www.sws.org)
and a subject students want to learn more about. From press stories
about conflicts between developers and conservationists to media reports
on heated debates in Congress over ecological funding, wetlands are
making the news. They are becoming widely recognized for their role in
flood storage, water quality improvement, recreation, and fisheries
support (e.g., Mitsch and Gosselink 2000), not to mention their function
as habitat for rare plants and animals. The regulation of wetlands as
“Waters of the United States” under Section 404 of the Clean Water
Act has led to an industry of environmental consultants, regulators, and
lawyers that identify and delineate wetlands, mitigate wetland impacts,
and develop and enforce wetland regulations and policy.
In my wetland ecology course at the University of
Maryland, I discuss the scientific and socioeconomic elements of this
complex, multidisciplinary subject. The basic sciences, which are the
primary emphasis in my course, include plant biology, hydrology, soil
science, biogeochemistry, ecosystem processes, and statistics and data
analysis. Because students may find work in private industry or
government, I also introduce the major aspects of applied wetland
science, including wetland creation, restoration, mitigation, and
assessment. Finally, because wetland scientists inevitably have to deal
with regulators and the general public, I touch on political and
economic issues related to wetlands.
The broad range of topics in wetland ecology is
difficult to deal with in a traditional classroom setting. While
lectures are critical for passing on technical and policy information in
a systematic manner, they are not well suited for teaching field or
laboratory techniques. To deal with the range of issues related to
wetland science, I use a combination of lecture and laboratory sessions
and occasional Saturday field trips.
Course Structure
The objective of the lecture, which meets one hour
per week, is to provide as much information as possible on the major
aspects of wetland science. (Click here to see a list of lecture topics
covered in the course.) Because of the
short time available for lecture, I rely heavily on Wetlands (Mitsch
and Gosselink 2000), which is widely considered to be one of the best
overall texts on the subject, and a publication on local wetlands (Tiner
and Burke 1995).
I begin the course with general information on
wetlands, such as how they can be defined, the general types of wetlands
that exist around the globe, the areal extent of wetlands, and wetland
impacts. In the remainder of the course, I deal mostly with the “science”
aspects of wetlands: their soil, hydrology, and plant and animal
communities. But even if the lecture were three hours per week, it would
not be possible to describe in sufficient detail the characteristics of
all the wetland types. I therefore have chosen to focus on salt and
brackish marshes for three reasons: (1) a tremendous amount of
scientific research has been done in these systems; (2) many of the
processes and factors operating in salt and brackish marshes are also
the same as those found in other wetland types (e.g., hydrologic effects
on decomposition and redox status, salinity effects on plants and
animals); and (3) they are an important wetland type in the mid-Atlantic
region and one that we see on field trips.
Finally, I introduce the applied wetland science
topics of wetland assessment, restoration, mitigation, and construction.
These topics are too broad to cover in any great detail (we have an
entire course in our program devoted solely to constructed wetlands);
however, we do visit restored and managed wetlands during the laboratory
period, and students often look at restored or constructed wetlands
during their group projects.
The bulk of class time is spent in the laboratory,
which meets four hours per week. The goals of the laboratory are
three-fold. First, I want students to see natural, restored, and managed
wetlands common in the mid-Atlantic coastal region. Second, I want them
to gain hands-on experience with common field techniques used in
sampling or describing wetland soil, vegetation, and hydrology (these
being three areas relevant to applied and basic wetland science). Last,
I want them to analyze, summarize, and present environmental data
effectively.
The laboratory is divided into two parts. During
the first part, which comprises about two-thirds of the semester, we
travel to various wetland sites, learn to identify wetland plants, and
collect plant, soil, and hydrologic data (table 1). We have visited
restored and natural, tidal and nontidal, and fresh and saline wetlands
(both swamps and marshes) within a few hours’ drive of our campus. The
methods we use are based on a number of sources (see table 1), which I
compile into simplified written procedures to streamline the labs. Data
collected during this part of the course are pooled; students e-mail me
their data in spreadsheet files, which I combine and send to the whole
class. Because we work in groups, replicate data are usually available
for each sample location. Each student prepares a lab report on some
aspect of the pooled data, and I give them individualized feedback on
their writing style, data analyses, tables, and graphs. Also during this
part of the semester, students work individually on a plant collection.
[For project descriptions, see “Lab Components” below.]
For the last third of the semester, the students
work in groups on a wetlands-related project of their choosing. At the
end of the semester, each group delivers a presentation on their project
accompanied by a detailed handout outlining their work complete with
maps, tables, and graphs.
|
Table 1. Overview of field and
laboratory activities for the wetland ecology course. |
| Topic |
Activity |
Equipment,
materials, and references |
| Plant taxonomy |
Taxonomic identification of
wetland plants |
Taxonomic references (e.g.,
Tiner 1993), dissecting kits, stereozoom microscopes |
| |
Collection, storage, and
preservation of plant specimens |
Drying ovens, plant presses,
blotters, and ventilators |
| |
Preparation of portable “mini-herbarium” |
Binders, plastic sheet
protectors, mounting paper, and tape or glue |
| Methods for vegetation
sampling and analysis |
Qualitative abundance
rankings |
Palmer et al. (1995) |
| |
Cover, density, frequency,
basal area, biomass; line-intercept and plot methods |
Quadrat sampling frames, tree
diameter tapes or calipers, measuring tapes, meter sticks, field
notebooks, knives, plastics bags, drying ovens, and plot markers
(Bonham 1989; Kent and Coker 1992) |
| |
Determination of hydrophytic
vegetation |
Environmental Laboratory
(1987); Reed (1988) |
| |
Calculations (species
richness and diversity, cover, basal area, density) |
Calculator or computer with
spreadsheet software (Peet 1974; Bonham 1989; Kent and Coker
1992) |
| |
Analysis and presentation of
wetland plant community data |
Computer with spreadsheet,
statistical, and charting software (Bonham 1989; Kent and Coker
1992) |
| Soil and hydrologic methods |
Determination of hydric soils |
Munsell soil color charts,
sharpshooter shovels, Dutch soil augers (U.S. Department of
Agriculture 1996) |
| |
Determination of wetland
hydrology |
Environmental Laboratory
(1987) |
| |
Bulk density, percent
moisture |
Cylindrical corers of known
volume, top- loading balances, drying ovens (Blake and Hartge
1986; Gardner 1986) |
| |
Salinity |
Salinity refractometers,
filter paper, 50-100 ml plastic syringes,
salinity-conductivity-temperature meters |
| |
Soil reduction tests |
Platinum electrodes,
reference electrodes, pH/ mV meters, a,a’-dipyiridil solution
for testing for reduced iron, nongalvanized nails (“rusty nail
test”) (Faulkner et al. 1989; Patrick et al. 1996) |
| |
Loss of organic matter on
ignition |
Muffle furnace, ceramic
crucibles, analytical balance (Nelson and Sommers 1996) |
| |
Relative elevation |
Auto level, stadia rods |
| |
Shallow groundwater level |
PVC pipe with slotted screen
or drilled holes, endcaps, soil augers, meter sticks |
Lab Components
Plant Taxonomy
The ability to distinguish and recognize plants typical of wetlands
is a critical tool for describing and delineating wetlands. While plant
communities of a particular area are a result of hydrology, soil,
climate, and other factors, plants are the most readily recognizable
feature of wetlands. For this reason, we begin learning common wetland
plants during the first laboratory session. Students collect plant
specimens, identify them using taxonomic keys or field guides, and
create pressed dried specimens. I require the Field Guide to Coastal
Wetland Plants of the Southeastern United States (Tiner 1993), which
contains excellent illustrations and descriptions, as well as
easy-to-use taxonomic keys.
Students are required to submit a collection of at
least 25 species of plants mounted and placed in plastic sheet
protectors in a three-ring binder. Specimens must include flowering or
fruiting material and leaves, and be labeled with scientific and common
names and location and date collected. After grading the plant
collections I return them so that the students will each have a “mini-herbarium”
they can use in the future. Invariably some students find this project
to be the most satisfying aspect of the course, possibly because a
successful collection requires an artistic sensibility that they rarely
have the opportunity to apply elsewhere in their studies.
Vegetation Sampling
Describing plant communities is necessary for delineating and assessing
wetlands for biological diversity, wildlife habitat value, and other
purposes. Working in groups of three to five people, students perform
qualitative, semiquantitative, and quantitative sampling in a number of
different wetland types (table 1). Measures of abundance used include
cover, density, frequency, and biomass of plant species determined using
plot and line-intercept techniques. Students also use the Corps of
Engineers Wetlands Delineation Manual (Environmental Laboratory
1987; can be downloaded from http://www.wes.army.mil/el/wetlands/)
and the National List of Plant Species that Occur in Wetlands
(Reed 1988; this version as well as the 1996 draft version can be
downloaded from http://www.nwi.fws.gov/bha/)
to determine if the areas they have sampled contain hydrophytic (i.e.,
wetland) vegetation.
In their lab reports, students gain experience
analyzing and presenting vegetation data. Working with vegetation data
is rarely a straightforward task because there are a number of ways to
analyze and present the data and there are multiple species to deal
with.
Soil and Hydrologic Methods
Again working in groups, students examine soils in soil pits or cores
for indicators of hydric (i.e., wetland) soils. The wetlands delineation
manual (Environmental Laboratory 1987) and Field Indicators of Hydric
Soils In the United States (USDA 1996; the 1998 version can be
downloaded from http://www.statlab.iastate.edu/soils/hydric/)
are used to identify and describe hydric soils. Soil samples are
collected and analyzed in the lab for organic matter content, bulk
density, and percent moisture (table 1). Soil salinity, an important
parameter in salt and brackish marshes, is measured in the field by
squeezing water from soil through filter paper in a large syringe and
determining salinity using a refractometer. Salinity of surface water or
water in cored holes is measured using a refractometer or a portable
salinity meter.
Quantifying the hydrology of a particular wetland
requires long-term measurement of hydrologic parameters, such as surface
water inflow and outflow, water level, and ground water flow. However,
there are several measurements that can be used to identify the presence
of wetland hydrology. One is the oxidation-reduction, or redox, status
of soils, which is a critical measure of the biogeochemical environment
of wetlands that is dependent on hydrology. Wetland soils are
predominantly anaerobic because of soil waterlogging, but contain areas
of aerobic conditions as well, which together create an environment
conducive to microbial transformation of substances. A simple but
visually effective way to demonstrate the chemically reducing
environment in wetlands is to stick large nongalvanized nails into
wetland and nearby upland soils, return in a few weeks, and observe the
amount of orange coloration on the nails. The upland nails will
typically be more orange (rusty, oxidized iron) than the wetland nails,
which will be pristine or contain dark patches (gray, reduced iron).
Another simple visual test is to use an a,a’-dipyiridil solution,
which turns pink when placed on soils containing reduced iron
(Environmental Laboratory 1987). A more quantitative approach is to use
platinum redox electrodes to measure redox potential, which can be
purchased or made (Faulkner et al. 1989; Patrick et al. 1996). The
meaning of the redox potential measurements seems to be clearer to
students after they have done the visual tests.
Other indicators of wetland hydrology are described
in the wetlands delineation manual (Environmental Laboratory 1987) that
can be used to determine if a particular area exhibits wetland
hydrology. These include observation of watermarks on trees, sediment
deposited on vegetation, drainage channels or scouring, standing water,
and saturated soils. Along with vegetation data, students analyze and
present soil and hydrologic data from these exercises in their lab
reports.
Group Project
Working in groups of three to five (not necessarily
the same groups as in the first portion of the course), students design
and implement a study of some aspect of wetland ecology. To help
students identify a project, I begin with a brainstorming activity where
I write potential project ideas on the board and discuss the problems
with or value of their various ideas. We have about a month in which to
collect data for a project, so time is a crucial consideration in
developing meaningful projects. We then break into groups for discussion
of these ideas, returning after about 30 minutes to the board to
identify broad group topics and assign class members to the various
groups. This phase of project development usually takes two to three
hours.
A week later, each group submits a brief proposal
that includes background literature on their topic, research questions
or hypotheses, and proposed methods. The methods can include those we
have experienced in lab or other techniques that they are familiar with
or want to learn. I review their proposals and work with the groups
individually over the course of a lab period to refine their study
design and methods. Some groups develop excellent research questions,
but I need to guide them toward something manageable and emphasize that
their projects will probably raise more questions than it will answer,
given the short time frame available (many ecological studies span
years). Other groups need input on asking relevant questions and
tailoring the methods to address those questions. Additional issues that
we deal with during this project development phase include selecting
study sites, deciding how many replicates they will have and how many
times they will sample, and adapting methods to best answer their
specific research questions.
After the groups finalize the experimental approach
to their project, they spend the bulk of the remaining three to four lab
periods and time outside of class collecting and analyzing data. This
allows them to make repeated measurements at their study sites. During
the last lab period, each group delivers a 30-minute presentation on
their project using slides, overheads, or a computer projector. Each
group also submits a handout to the entire class that includes a
detailed written outline of their project as well as figures and tables.
The format of the handout follows typical scientific format
(Introduction, Methods, Results, and Discussion), although I generally
urge them to combine results and discussion for the presentation. The
presentations usually occupy an entire four-hour lab period because of
questions, discussion, technical glitches, and a break halfway through.
When given the freedom to come up with research
ideas, many of my students rose to the occasion and went beyond what was
necessary to create exceptional projects (fig. 1). The topics they have
chosen encompass basic ecological questions as well as aspects of
applied wetland science, such as functional assessment, wetlands
delineation, and wetland construction and restoration.
|
Figure 1. Examples of group
projects in the wetland ecology course. |
-
Nutrient removal and transformation
in natural and restored tidal freshwater wetlands
-
Comparison of delineation
techniques in two wetland systems
-
Impacts of landscape position on
the health of coastal wetlands
-
Vegetation, soil characteristics,
and water quality of riparian wetlands in agricultural and
urban settings
-
The effectiveness of storm water
treatment wetlands in improving water quality
-
Comparison of soils, vegetation,
and hydrology of restored and natural wetlands
-
Impacts of highway-induced
fragmentation on wetland plant communities and soils
-
Effects of elevation on vegetation,
soil, and hydrology in a floodplain forest
-
Relationships between river
discharge and annual variation in plant community structure in
a tidal wetland
-
Effects of hydrologic modification
from stream channel diversion on wetland soil and vegetation
-
Relationships between soil
characteristics and plant species diversity in a forested
wetland
-
Use of the Hydrogeomorphic
assessment technique (HGM) to evaluate two restored tidal
wetlands
-
Comparison of water quality
functions in an urban stormwater treatment wetland and a
natural wetland
-
Bird communities of a restored and
a natural freshwater wetland
-
Relationships between dominance of Phragmites
australis, plant species diversity, and environmental
conditions in urban wetlands
|
What Works and What Doesn’t
A common thread appeared after two years of
responses to course evaluation questions: students find the hands-on
aspect of the course very useful. Written student comments on
end-of-semester evaluations included “Field experience was great!”
and “Fieldwork aspect is very useful!” Some students also told me
that analyzing and presenting data from a project they had designed and
implemented was a great experience and that the presentations were the
best they had seen in any class. Responses on student evaluations
supported this, indicating that the lab activities were valuable in
increasing their experimental design, data analysis, and communication
skills (table 2).
|
Table 2. Summary of student
responses to end-of-semester evaluation questions pertaining to
the wetland ecology laboratory in 1998 and 1999 (questions
pertaining to lecture portion of the course are not listed). |
|
Scores were: 5 = agree strongly, 4 =
agree, 3 = neutral, 2 = disagree, 1 = strongly disagree. |
| Question |
Mean |
Standard Error |
N |
| This course
increased your: |
|
|
|
| |
ability to apply math |
4.0 |
0.33 |
12 |
| |
ability to apply basic
science |
4.2 |
0.55 |
22 |
| |
knowledge of computer skills |
3.9 |
0.89 |
15 |
| |
ability to write effectively |
3.8 |
0.44 |
24 |
| |
ability to speak
effectively |
4.2 |
0.45 |
24 |
| |
ability to design/conduct
experiments |
4.3 |
0.67 |
24 |
| |
ability to analyze and
interpret data |
4.3 |
0.69 |
23 |
| |
appreciation of the need to
engage in lifelong learning |
4.2 |
0.47 |
20 |
| Instructor
emphasized conceptual understanding of the experimental method and
its use in laboratory exercises |
4.5 |
0.62 |
24 |
| Instructor gave
a clear description of the lab/studio exercises to be
performed |
3.9 |
0.53 |
24 |
| The lab/studio
exercises increased your interest in the course
material/topics |
4.8 |
0.80 |
24 |
| The time spent
in lab/studio was used effectively |
4.4 |
0.65 |
24 |
| The studio/lab
was well equipped for the exercises required |
4.6 |
0.79 |
24 |
| Lab
reports/write-ups were returned in a timely manner |
4.1 |
0.49 |
24 |
On the negative side, this course can be difficult
to schedule because it is hard to predict how much time will be required
for field and lab activities and administering the group project. Thus,
some level of disorganization usually occurs, although this has improved
with repeated teaching of the course. For example, I have had to shift
due dates for some of the assignments and field trips because they
conflicted with my original dates for starting the group project. One
student commented, “The class lab project could have been better
structured.” Some students also were unclear about how to approach the
lab report, which is based on data collected on various parameters at a
range of sites during the first portion of the course. One student “found
requirements for lab report vague” and another said politely, “Making
the lab report description clearer would be helpful.” Students find it
difficult to write the lab report in standard scientific format because
the data do not fit neatly into a single hypothesis or question, but I
view this as a valuable exercise because the students have to think
about the data they want to analyze rather than follow a “cookbook”
lab report model.
Another issue is the time required to find field
sites, work out the details of the methods, and obtain the necessary
equipment. After teaching the course several times, however, I found
that my time input has decreased, with only minor modifications
necessary to keep the course up-to-date and interesting (for me as well
as the students!).
I concluded from both the course evaluations and my
years of teaching that wetland ecology is a course that greatly benefits
from field and laboratory activities. Most regions of the world contain
wetlands, and field and laboratory exercises relating to soil,
vegetation, and hydrology are easy to do and do not require expensive or
complicated equipment. I have found that coupling lectures with an
excellent textbook is an efficient means of passing on scientific and
technical information to students, and field and laboratory activities
help them to see the connection to that information. The fieldwork also
gives students knowledge of an ecosystem that cannot be conveyed in a
classroom lecture. The colors, sounds, smells, and textures experienced
in a real wetland leave a lasting impression that make the facts and
figures all the more relevant.
Andrew Baldwin is an assistant professor
of natural resources management, department of biological resources
engineering, University of Maryland, College Park, MD 20742; e-mail: ab174@umail.umd.edu.
Acknowledgments
The author would like to thank Irv Mendelssohn
of Louisiana State University for teaching excellent wetland courses
that influenced his own teaching style, Steve Faulkner, also of LSU, for
helping with techniques related to wetland biogeochemistry, soil, and
hydrology, and Paula Tanner Baldwin and anonymous reviewers for helpful
comments on the manuscript.
|
Lecture topics covered
in this course |
| Definitions of wetlands: regulatory, ecological,
management |
|
Types of wetlands and general characteristics |
|
Wetland distribution, extent, changes, and impacts |
Detailed study:
- Salt and brackish marshes
- Geographical distribution
- Geomorphology and hydrology
- Biogeochemical processes
- Plant and
animal communities
- Ecosystem processes
|
Other wetland
types, with emphasis on major factors differing from salt and
brackish marshes:
- Tidal and nontidal freshwater wetlands (marshes and
swamps);plant adaptations to flooding
- Mangrove forests; plant adaptations to salinity
|
| Overview of
wetland types: generalities and specifics |
| Applied wetland
science (functional assessment, mitigation, and construction and
restoration techniques) |
References
Bonham, C.D. 1989. Measurements for Terrestrial
Vegetation. New York: John Wiley & Sons.
Blake, G.R., and K.H. Hartge. 1986. Bulk density. In Methods of Soil
Analysis, Part 1. Physical and Mineralogical Methods, ed. A. Klute,
363-375. 2nd ed. Madison, WI: Soil Science Society of America.
Cahoon, L.B. 1996. Using stormwater detention ponds for aquatic science
instruction. Journal of College Science Teaching 26:115-118.
Camill, P. 2000. Using journal articles in an environmental biology
class. Journal of College Science Teaching 30:38-43.
Environmental Laboratory. 1987. Corps of Engineers Wetlands
Delineation Manual. Technical Report Y-87-1. Vicksburg, MS: U.S.
Army Engineers Waterways Experiment Station.
Faulkner, S.P., W.H. Patrick, Jr., and R.P. Gambrell. 1989. Field
techniques for measuring wetland soil parameters. Soil Science
Society of America Journal 53:883-890.
Ferrier, M.D. 1989. Planning and implementing undergraduate field
experiences in tropical marine science. Journal of College Science
Teaching 18:368-426.
Gardner, W.H. 1986. Water content. In Methods of Soil Analysis, Part
1. Physical and Mineralogical Methods, ed. A. Klute, 493-544. 2nd
ed. Madison, WI: Soil Science Society of America.
Gill, R.A., and I.C. Burke. 1999. Using an environmental science course
to promote scientific literacy. Journal of College Science Teaching
29:105-110.
Grove, J. 1984. Environmental biology: A field experience. Journal of
College Science Teaching 13:150-153.
Kent, M., and Coker, P. 1992. Vegetation Description and Analysis: A
Practical Approach. New York: John Wiley and Sons.
Kerr, E. 1996. Exploring wetlands. Green Teacher 47:34-37.
Lopushinsky, T., and L. Besaw. 1986. Field experiences for nonscience
students. Journal of College Science Teaching 16:21-24.
Mitsch, W.J., and J.G. Gosselink. 2000. Wetlands. 3rd ed. New
York: John Wiley and Sons.
Nelson, D.W., and L.E. Sommers 1996. Total carbon, organic carbon, and
organic matter. In Methods of Soil Analysis, Part 3. Chemical Methods,
ed. D.L. Sparks, 961-1010. Madison, WI: Soil Science Society of America.
O’Neal, L.H. 1995. Using wetlands to teach ecology & environmental
awareness in general biology. American Biology Teacher
57:135-139.
Palmer, M.W., G.L. Wade, and P. Neal. 1995. Standards for the writing of
floras. BioScience 45:339-345.
Patrick, W.H., R.P. Gambrell, and S.P. Faulkner. 1996. Redox
measurements of soils. In Methods of Soil Analysis, Part 3. Chemical
Methods, ed. A. Klute, 1255-1273. Madison, WI: Soil Science Society
of America.
Peet, R.K. 1974. The measurement of species diversity. Annual Review
of Ecology and Systematics 5:285-307.
Reed, P.B. 1988. National List of Plant Species that Occur in
Wetlands: Northeast (Region 1). Biological Report 88(26.1).
Washington, D.C.: U.S. Fish and Wildlife Service.
Stephens, L.J., W.J. Lindsay, G.C. Hall, L.B. Kass, L. Simons, and R.C.
Ulsh. 1988. Marine and island ecology. Journal of College Science
Teaching 18:18-21.
Stewart, P. 1998. The call of the wetlands. Green Teacher
55:23-27.
Switzer, P.V. 1995. Campus field trips: An effective supplement to
classroom instruction. Journal of College Science Teaching
25:140-143.
Texley, J. 1988. Our valuable wetlands. The Science Teacher
55:19-29.
Tiner, R.W. 1993. Field Guide to Coastal Wetland Plants of the
Southeastern United States. Amherst, MA: The University of
Massachusetts Press.
Tiner, R.W., and D.G. Burke. 1995. Wetlands of Maryland. U.S.
Fish and Wildlife Service, Ecological Services, Region 5, Hadley, MA,
and Maryland Department of Natural Resources, Annapolis, MD.
U.S. Department of Agriculture (USDA) and Natural Resources Conservation
Service (NRCS). 1996. Field Indicators of Hydric Soils in the United
States. Fort Worth, TX: USDA, NRCS.