
In this state where
natural habitats have been all but obliterated through conversion to cropland,
Iowa's endangered species legislation has a vital role to play. However, the
information pertaining to
rare species legislation comprises a relatively extensive and complex data set
that is largely inaccessible because the sources are government publications,
unpublished reports and professional correspondence. The
purpose
of this website and database is to make these data readily available in an interactive
format and to include background information that provides a useful context
for evaluating revisions of the endangered and threatened plant species list
when they are proposed. A second phase of this project is underway and involves
development of a database of all the University of Iowa Herbarium Iowa collections'
data, particularly distributional information, and to make these available in
an interactive format that will include county range maps.
The database is a compilation of information on rare Iowa plants from four sources. These sources include (see Literature Cited for bibliographic details):
five Iowa Administrative Code lists of endangered and threatened plant species (Iowa Administrative Code 1977, 1984, 1986, 1988, 1994)
1998 list proposed to supercede the 1994 Iowa Administrative Code list (J. Pearson, Iowa DNR (Department of Natural Resources), in litt. 1998)
1998 candidate list (J. Pearson, Iowa DNR, in litt. 1998)
lists from three endangered and threatened plant reports (Roosa & Eilers 1978, Roosa, Pusateri & Eilers 1986, and Roosa, Leoschke & Eilers 1989)
Five groups of plants/plant-like organisms -- vascular plants ('higher' plants), mosses, hepatics (liverworts), lichens, and fungi (mushrooms/toadstools) -- are included in the database; however, most of the data pertain to vascular plants, which is the only group included in the Iowa Administrative Code lists of endangered and threatened plants. Organized by plant/plant-like group, the data include:
Latin species name according to source (see above). Source names are abbreviated as follows: Iowa Administrative Code (IA Adm. Code), proposed list of 1998 (DNR Prop. List 1998), candidate list of 1998 (DNR Cand. List 1998), and reports on endangered and threatened
plants (E & T Report).
Latin family name according to Eilers and Roosa (1994), The Vascular Plants of Iowa. If the family name in Kartesz (1999), A Synonymized Checklist and Atlas with Biological Attributes for the Vascular Flora of the United States, Canada, and Greenland, is different, it is included in brackets.
common name according to Eilers and Roosa (1994), and also Gleason and Cronquist (1991) ), Manual of Vascular Plants of the Northeastern United States and Adjacent Canada, and Kartesz (1999), if the latter two differ from Eilers and Roosa.
category (e.g., endangered, threatened, special concern, extirpated) assigned in each source (Iowa Administrative Code lists, 1998 proposed list, 1998 candidate list, and reports on endangered and threatened plants).
Latin species name accepted by Eilers and Roosa (1994)
Latin species name accepted by Gleason and Cronquist (1991)
Latin species name accepted by Kartesz (1999)
Latin species name according to source
Latin family name according to Anderson, Crum and Buck (1990), List of the mosses of North America north of Mexico, and Anderson (1990), A checklist of Sphagnum in North America north of Mexico.
category assigned in 1998 proposed and candidate lists.
Latin species name accepted by Anderson, Crum and Buck (1990) and Anderson (1990), except in a few instances when more recent taxonomic and nomenclatural changes have been incorporated.
Latin species name according to source
Latin family according to Stotler and Crandall-Stotler (1977), A checklist of the liverworts and hornworts of North America.
category assigned in 1998 proposed and candidate lists.
Latin species name accepted by Stotler and Crandall-Stotler (1977)
Latin species name according to source
category assigned in 1998 proposed and candidate lists.
Latin species name accepted by Esslinger and Egan (1995)
Latin species name according to source
Latin family according to Miller and Farr (1975), An index of the common fungi of North America.
category assigned in 1998 proposed and candidate lists.
Latin species name accepted by Miller and Farr (1975)
The
tables below summarize data in five Iowa Administrative Code lists of endangered
and threatened plant species (IA Adm. Code 1977, 1984, 1986, 1988, 1994), a
1998 list proposed by the Iowa DNR (Department of Natural Resources) to supercede
the 1994 Iowa Administrative Code list (DNR Prop. List 1998), a 1998 candidate
list by the Iowa DNR (DNR Cand. List 1998), and lists from three endangered
and threatened plant reports (E & T Report 1978, 1986, 1989). Category abbreviations
(e.g., E for endangered, T for threatened, SC for special concern, X for extirpated,
etc.) correspond to those in the database.
|
SOURCE & YEAR CATEGORY |
IA
Adm. Code 1977 |
E
& T Report 1978
|
IA
Adm. Code 1984
|
IA
Adm. Code 1986
|
E
& T Report 1986
|
IA
Adm. Code 1988
|
E
& T Report 1989
|
IA
Adm. Code 1994
|
DNR
Prop.
List 1998 |
DNR
Cand. List 1998 |
| Endangered (E) |
100
|
101
|
123
|
123
|
123
|
140
|
137
|
64
|
16
|
|
| Threatened (T) |
52
|
51
|
56
|
56
|
56
|
58
|
58
|
89
|
93
|
|
| Special Concern (SC) |
|
|
|
|
33
|
28
|
29
|
227
|
167
|
|
|
Extirpated
(X) |
|
69
|
|
|
49
|
|
45
|
|
|
|
| Undetermined (UnD) |
|
25
|
|
|
|
|
|
|
|
|
| Candidate Species (C) |
|
|
|
|
|
|
|
|
|
538
|
| TOTAL E + T |
152
|
152
|
179
|
179
|
179
|
198
|
195
|
153
|
109
|
|
| TOTAL E + T + X |
|
221
|
|
|
228
|
|
240
|
|
|
|
|
SOURCE & YEAR CATEGORY |
IA
Adm. Code 1977 |
E
& T Report 1978
|
IA
Adm. Code 1984
|
IA
Adm. Code 1986
|
E
& T Report 1986
|
IA
Adm. Code 1988
|
E
& T Report 1989
|
IA
Adm. Code 1994
|
DNR
Prop.
List 1998 |
DNR
Cand. List 1998 |
| Endangered (E) |
3
|
|
||||||||
| Threatened (T) |
25
|
|
||||||||
| Special Concern (SC) |
28
|
|
||||||||
|
Extirpated (X) (incl. Presumed Extirpated, PsX, and Possibly Extirpated, PoX) |
|
|
||||||||
| Undetermined (UnD) |
|
|
||||||||
| Candidate Species (C) |
|
135
|
||||||||
| TOTAL E + T |
28
|
|
||||||||
| TOTAL E + T + X |
|
SOURCE & YEAR CATEGORY |
IA
Adm. Code 1977 |
E
& T Report 1978
|
IA
Adm. Code 1984
|
IA
Adm. Code 1986
|
E
& T Report 1986
|
IA
Adm. Code 1988
|
E
& T Report 1989
|
IA
Adm. Code 1994
|
DNR
Prop.
List 1998 |
DNR
Cand. List 1998 |
| Endangered (E) | 0 | |||||||||
| Threatened (T) | 7 | |||||||||
| Special Concern (SC) | 6 | |||||||||
|
Extirpated
(X) |
||||||||||
| Undetermined (UnD) | ||||||||||
| Candidate Species (C) | 32 | |||||||||
| TOTAL E + T | 7 | |||||||||
| TOTAL E + T + X |
|
SOURCE & YEAR CATEGORY |
IA
Adm. Code 1977 |
E
& T Report 1978
|
IA
Adm. Code 1984
|
IA
Adm. Code 1986
|
E
& T Report 1986
|
IA
Adm. Code 1988
|
E
& T Report 1989
|
IA
Adm. Code 1994
|
DNR
Prop.
List 1998 |
DNR
Cand. List 1998 |
| Endangered (E) |
0 |
|||||||||
| Threatened (T) |
0 |
|||||||||
| Special Concern (SC) |
1 |
|||||||||
|
Extirpated
(X) |
||||||||||
| Undetermined (UnD) | ||||||||||
| Candidate Species (C) |
1 |
|||||||||
| TOTAL E + T |
0 |
|||||||||
| TOTAL E + T + X |
|
SOURCE & YEAR CATEGORY |
IA
Adm. Code 1977 |
E
& T Report 1978
|
IA
Adm. Code 1984
|
IA
Adm. Code 1986
|
E
& T Report 1986
|
IA
Adm. Code 1988
|
E
& T Report 1989
|
IA
Adm. Code 1994
|
DNR
Prop.
List 1998 |
DNR
Cand. List 1998 |
| Endangered (E) | 0 | |||||||||
| Threatened (T) | 0 | |||||||||
| Special Concern (SC) | 3 | |||||||||
|
Extirpated (X) (incl. Presumed Extirpated, PsX, and Possibly Extirpated,PoX) |
||||||||||
| Undetermined (UnD) | ||||||||||
| Candidate Species (C) | 3 | |||||||||
| TOTAL E + T | 0 | |||||||||
| TOTAL
E + T + X |
One frequently hears
the assertion that 'Iowa is the most altered state in the union', in reference
to the devastation of natural habitats since the time of European settlement.
The validity of this statement is evident at a glance on the NRCS
(Natural Resources Conservation Service) map showing Percent of Non-Federal
Area in Cropland. Only Illinois, and perhaps Indiana, rival Iowa in the areal
extent of cropland. In Iowa, estimates are that less than one-tenth of one percent
of the tallgrass prairie (and virtually none of the savanna) that covered approximately
83% of the landscape remains today1.
Similarly, less than three-tenths of a percent of the natural wetlands that
comprised perhaps 6% of the surface area remain2.
On the surface, the forests appear to have fared
somewhat
better, with approximately fifty percent of the original surface area of 11%
still wooded3; however, this
figure is misleading since much, if not most, of the natural forests have been
altered by logging and other management activities. Analyses of 1998 Landsat
images by the Iowa Department of Natural Resources Geological Survey Bureau
(ftp://ftp.igsb.uiowa.edu/pub/download/
land_cover/cntytot.xls)
reveals that 60% of today's dramatically altered Iowa landscape is comprised
of row crops; 31% is pastures/lawns; and 2% is roads/buildings. Manmade wetlands
comprise approximately .3% of the surface area4.
European settlement marks the beginning of wholesale habitat destruction in Iowa, and also the initiation of alien species introductions. Naturalized alien species, that is, ones that have escaped from cultivation and invaded natural habitats where they wreak havoc on remnants of natural vegetation, are probably as great a threat to native species diversity as habitat destruction. Notable examples in Iowa presently include Garlic Mustard (Alliaria petiolata (Bieb.) Cavara & Grande), Leafy Spurge (Euphorbia esula L.), and Purple Loosestrife (Lythrum salicaria L.), three species that are decimating the native species in woodland, prairie and wetland habitats, respectively. According to Eilers and Roosa (1994), 1,958 species of vascular plants have been recorded from Iowa; however, 442 of these are alien, while 1,516 are native. Lewis (1998) noted that 54 additional species have been recorded since the publication of Eilers and Roosa's checklist (Eilers & Roosa 1994), of which eight are alien and 46 are indigenous. More recently, another 39 alien and 12 indigenous species were recorded (Norris et al. 2001). In addition, there are a few more unpublished records (e.g., Horton, Cady and Madsen, unpublished data). Updating Eilers and Roosa's (1994) figures, the current flora is over 2,063 species, of which 489 are alien and 1,574 native. Thus, 24 percent of the species recorded from Iowa are not native. Kartesz' (1999) total of 2,059 species is very close; however, his figure of 405 alien species is slightly lower, but even so, 20 percent are alien. Either way, one-fifth to one-quarter of the plants recorded from this state are naturalized alien species, some of which are having a dramatic, detrimental impact on populations of native species.
Based on Kartesz' (1999) figures, Iowa's native flora (1,654 species) is slightly larger than those of North and South Dakota, and Nebraska (1191, 1486 and 1496 species, respectively), slightly smaller than Minnesota, Wisconsin and Kansas (1840, 1908 and 1794, respectively), and quite a bit smaller than Illinois and Missouri (2313 and 2136, respectively). However, on the basis of surface area, Wisconsin is slightly smaller than Iowa, Illinois is slightly larger, and larger still are Missouri, North Dakota, South Dakota, Nebraska, Kansas and Minnesota (from smallest to largest). Obviously, floristic diversity reflects other factors in addition to surface area. The two that probably have had the greatest impact are physiography, the contours of the land, and phytogeography, the ecological and historical factors that have shaped the vegetation.
Undoubtedly, Iowa's
floristic diversity is influenced by the diversity of landform regions documented
by Prior (1991), and particularly by the physiographic complexity of the Paleozoic
Plateau in the northeastern part of the state and the Loess Hills in the west.
Phytogeographically, Iowa is in a
transition
zone, the ecotone between deciduous forest and prairie, so both eastern and
western elements reach the edges of their ranges here. In addition, boreal/northern
hardwoods elements extend into the state, particularly in the Paleozoic Plateau,
where the cold air (algific talus) slopes provide cooler microsites. Eilers
and Roosa (1994) recognized these same elements and also an Ozarkian woodland
element. With the data in Kartesz and Meacham's Synthesis of the North America
Flora (1999), it is possible to quantitatively analyze the affinities of the
Iowa vascular plant flora relative to that of each state and province in North
America north of Mexico. The similarity ranks on the accompanying map represent
simplified Sørensen similarity indices5
calculated from data in Kartesz and Meacham (1999). Floras with the greatest
number of species in common with Iowa have lower numbers and are shaded darker,
while those with fewer species in common have higher numbers and lighter shading.
As one might expect, the floras of Minnesota, Wisconsin and Illinois are most
similar to that of Iowa, but Indiana is equally similar, while Missouri and
Nebraska are no more so than Ohio and Michigan. At the next level (similarity
rank of three), Kansas is no more similar than Pennsylvania, New York, Connecticut
and Ontario, while North and South Dakota are less similar still and equivalent
to Kentucky, West Virginia, New Jersey and Massachusetts. Clearly, the strongest
affinities of the Iowa flora are to the east and northeast, with strong similarities
extending as far as the eastern seaboard. In contrast, there is a relatively
abrupt decrease in similarity to the west in Montana, Wyoming, Colorado and
New Mexico, and this decline is much greater than that to the south and southeast,
where, with the exception of Florida, even the states from Louisiana to North
Carolina have higher levels of similarity than western states that are much
closer geographically.
Considering that Iowa
lies on the eastern border of the Great Plains, and historically over 80 percent
of the surface area of the state was prairie, it is noteworthy that the strongest
floristic similarities are
with
states that were dominated by deciduous and boreal/northern hardwoods forest.
Almost certainly, these latter elements account, in great part, for the relative
richness of the Iowa flora by comparison to North and South Dakota, and Nebraska,
even though these states have a greater surface area. In addition, a significant
number of the species that are largely restricted (in Iowa) to the Driftless
Area in northeastern Iowa also are among the rarest species in the state (see
maps in Pusateri, Roosa and Farrar, 1993). Thus, these boreal/northern hardwoods
forest elements may account for a significant proportion of the historically
rare species recorded from Iowa.
In the reports on
Endangered and Threatened Vascular Plants (Roosa & Eilers 1978, Roosa et al.
1986, and Roosa et al. 1989), 91 species are listed as either extirpated,
presumed or possibly extirpated, although extant populations of some of these
have been found subsequently. It is apparent that a significant number of plants
would have been rare in Iowa historically simply because of the phytogeographic
position of
the state. However, the impact of habitat destruction and naturalized alien
species has ensured that naturally rare species have become even rarer. For
example, Low Bindweed (Calystegia spithamea (L.) Pursh) has been recorded
from nine counties, but only four of these are based on post-1950 records (Roosa,
Leoschke and Eilers 1989). And some surely have been extirpated, for example,
Pod Grass (Scheuchzeria palustris L. var. americana Fern.). Given
the on-going urban sprawl into rural areas, if we are to preserve the dwindling
biodiversity and remnants of natural habitats that represent the natural heritage
of this state, it is vital that effective legal protection be provided.
Herbarium
specimens. Scientists and knowledgeable laypersons preserve collections
(samples) of living plants and these are maintained in repositories called herbaria
(e.g., the University of Iowa Herbarium was such a repository).
Each
specimen is labelled with the locality where it was collected and serves as
a permanent record of the occurrence of that species at a particular site and
point in time. Since each specimen documents a single site, it is necessary
to collect one at each locality where the species occurs. Collections make it
possible to re-evaluate the data (records of the occurrence of species) at any
time by examining a specimen. If a record is based solely on a verbal or written
communication, it is impossible to determine whether that record is valid, i.e.,
whether the identification is correct. In most instances, even a photographic
record is insufficient documentation simply because many characters useful for
identification are too small to be decipherable (or are obscured) in a photograph
or they require accurate measurements that are impossible to obtain from a photograph.
Thus, collections are the vital link with the natural world and they provide
a sound, scientific foundation for all decisions regarding rare species.
The need for collections
presents a conundrum. Are the species we want to preserve going to become even
rarer as a result of documenting their occurrence with collections? First, specimens
of state (and federal) listed species cannot be taken legally without a Scientific
Collector's Permit issued by the Iowa Department of Natural Resources. Beyond
that, specimens of rare species should not be collected
without careful investigation of the size of the population and making sure
the site has not been documented already by another investigator. Size of the
population is a judgement call, and it also can be a complicated issue with
plants. For one thing, populations of some plants fluctuate markedly from year
to year. Also, what appears to be a reasonably large population, for example,
one comprised of perhaps 100 individuals, may actually represent just a few
genetic individuals because multiple plants are connected below-ground. Another
consideration is whether the plant is an annual or perennial. If it is an annual,
the long-term impact of removing a plant is less than if it is a perennial because
the annual will die at the end of the growing season. Ordinarily, plant specimens
should include the entire plant, roots and all; however, the destructive effects
of making a collection of a rare, perennial plant can be mitigated by removing
only the above-ground parts, because some plants can regenerate from the roots
the following year.
Humans are one of
10 to 100 million species that inhabit the earth (Wilson 1992). Fewer than two
million species have been described and we know virtually nothing beyond the
names of most of those already documented, nothing of the potential economic
and medical benefits they might provide (Wilson 1992).
While
most North American species of plants have been described, even in a state as
small as Iowa and with as few natural habitats remaining, we still are finding
previously undescribed species (albeit rarely), new state records for some (e.g.,
a population of Southern Adder's-tongue (Ophioglossum vulgatum L.) was
discovered in southeast Iowa in 1994, Horton unpublished data), and county records
for numerous species. And we have much to learn about the ecological role of
the species that occur here. The remnants of natural habitats and the biodiversity
they harbour are the natural heritage of this state and country. Learning about
them -- which species are present; which species are rare; why some are common
and some rare; the factors that control each species' occurrence; how each influences
the occurrence of other species -- enriches our lives.
In 1973, the United States Endangered Species Act provided federal protection for plants as well as animals, and in 1975, the Iowa Legislature passed the Endangered Wildlife and Plants Act (Iowa Acts and Joint Resolutions 1975), which required the following:
|
The State Conservation Commission [presently the Natural Resource Commission] "shall perform those acts necessary for the conservation, protection, restoration, and propagation of endangered and threatened species...". The Director of the State Conservation Commission [presently the Director of the Department of Natural Resources] "shall conduct investigations on fish, plants and wildlife in order to develop information relating to population, distribution, habitat needs, limiting factors, and other biological and ecological data to determine management measures necessary for their continued ability to sustain themselves successfully". |
|
|
The Commission "shall review the state list of endangered and threatened species at least every two years and may amend the list". The Director "shall establish programs, including acquisition of land or aquatic habitat, necessary for the management of endangered and threatened species". |
Subsequently, the
Management and Protection of Endangered Plants and Wildlife (Code of Iowa 1977)
mandated
preparation of a list of "fish, plants, and wildlife which are determined to
be endangered or threatened within the state". The Iowa Administrative Code
listings of Endangered and Threatened Plant Species, the first of which was
published in 1977, provide legal protection for rare species, and the lists
have proven crucial in preventing further destruction. For example, the Iowa
Department of Transportation was required to reroute the Highway 63 Bypass around
Eddyville because a population of the state threatened, Tubercled Orchid (Platanthera
flava (L.) var. herbiola (R. Br.) Luer) was discovered in the path
of the proposed bypass.
To date, five lists of endangered and threatened species have been published in the Iowa Administrative Code, in 1977, 1984 and 1986 (the latter two are identical), 1988 and 1994, and a sixth was proposed in 1998, but subsequently cancelled in response to public protest (written comments submitted to the Iowa DNR). In addition, in 1998, a list of 'candidate' species was circulated with the proposed list. There also are three reports on endangered and threatened plants, from 1978 (Roosa & Eilers 1978), 1986 (Roosa, Pusateri & Eilers 1986) and 1989 (Roosa, Leoschke & Eilers 1989), that correspond to the Iowa Administrative Code lists of 1977, 1984-86, and 1988. Only vascular plants were included in the five published lists; however, the 1998 proposed list also incorporated mosses, hepatics (liverworts), fungi (mushrooms/toadstools) and lichens.
The
federal lists of endangered and threatened
species provide
a continental perspective. Their focus is on species that are rare if one considers
the country as a whole. Some of these species may be locally abundant at individual
localities or even in some states; Northern Wild Monkshood (Aconitum noveboracense
Gray) is one such species that occurs in Iowa. State lists are, by their very
nature, constrained to a provincial focus. Their role is at the local level.
Five species are federally
listed, all as threatened. They are: ![]()
Northern Wild Monkshood (Aconitum noveboracense Gray)
Mead's Milkweed (Asclepias meadii Torrey ex Gray)
Prairie Bush Clover (Lespedeza leptostachya Engelm.)
Eastern Prairie Fringed Orchid (Platanthera leucophaea (Nutt.) Lindley)
Western Prairie Fringed Orchid (Platanthera praeclara Sheviak & Bowles)
Three categories, endangered, threatened and special concern, are used in the Iowa Administrative Code lists, but only species designated endangered and threatened have legal protection in Iowa. Endangered and threatened are defined in Iowa as they are federally. The special concern category was introduced in the 1988 Iowa Administrative Code and provides no legal protection. It is not used in the federal listings. Two other categories, extirpated (including presumed and possibly extirpated) and undetermined, are used in at least one of the three Endangered and Threatened Plant reports (Roosa & Eilers 1978, Roosa, Pusateri & Eilers 1986, Roosa, Leoschke & Eilers 1989), but not the Iowa Code or federal lists.
The functional criteria
for determining whether a species will be included in the Iowa Administrative
Code
lists of endangered and threatened species are not given in the Code. It simply
is stated that "The natural resource commission, in consultation with scientists
with specialized knowledge and experience, has determined the following animal/plant
species to be endangered, threatened or of special concern" (Iowa Administrative
Code 1994). However, the primary criterion for the five Code plant lists published
to date (1977 through 1994) has been rarity; that is, species known from a limited
number of sites are listed.
The Code lists from
1977, 1984 and 1986 (the latter two are identical), and 1989 correspond to three
reports on rare plants by Roosa and Eilers (1978), Roosa, Pusateri and Eilers
(1986) and Roosa, Leoschke and Eilers (1989). All three contain distributional
information for each species, and the second and third include county
dot maps, with closed circles representing post-1950 records or extant occurrences
and open circles representing pre-1950 records or sites known to have been destroyed.
The dot maps are based on verifiable herbarium records, literature citations,
and also sight records (someone has seen the plant, but there is no specimen
record). Species designated endangered or threatened in these reports generally
are known from less than five extant sites (~=counties), although a few are
known from eight or nine because other factors were taken into consideration.
When the 1994 Code list was proposed in 1993, Dr. John Pearson of the Iowa Department
of Natural Resources (DNR) circulated a "Rationale for listing of plant species
as Endangered, Threatened, and Special Concern" (J. Pearson in litt.
1993). Again, the primary criterion was rarity: if a species occurred in five
or fewer counties based on recent (post-1950) records, it would be considered
for listing . Dr. Pearson reported that 387 species met this criterion (as in
the rare plant reports cited above, in practice, some species considered for
listing actually were known from more than five counties); however, an additional
factor, 'Inventory Bias', also was taken into consideration. This was based
on the premise that general inventories of sites result in collection bias.
That is, species that are problematic taxonomically and those that occur in
'under-inventoried habitats', specifically, disturbed and aquatic habitats,
will be under-represented in collections. When species in these categories were
removed, a total of 151 species were left(J. Pearson in litt.
1993).
In the Code lists from 1977, 1984 and 1986, and 1989, a noteworthy exception
to the rarity criterion is that species listed as extirpated (also presumed
extirpated or possibly extirpated) in the rare plant reports (a total of 91
species in the three reports) are not included in the Code. These species are
included in the 1994 Code list; however, they are designated special concern,
so they have no legal protection if extant populations are found.
In
October of 1998, a fifth list of endangered and threatened plant species was
proposed, and Dr. Pearson
provided a discussion of selection criteria and a list of candidate species
(J. Pearson in litt. 1998). Although rarity was a fundamental criterion
for placing a species on the candidate list, additional criteria were applied
subsequently and these focused on 'natural habitats' and a 'regional perspective'.
Species that occur in disturbed habitats were excluded from consideration, on
the premise that disturbance-adapted species are more likely to persist. Species
that occur only
in the outer two tiers of counties were excluded, because they are presumed
to be more common in adjacent states.
This 1998 proposed list was cancelled in early 1999 in response to public protest
(written comments submitted to the Iowa DNR). Subsequently, Drs. Pearson and
Daryl Howell organized a "State Endangered Species Expert Workshop",
which was held on April 22, 1999. The Workshop was comprised of a series of
presentations, and a short question/discussion period. Subsequently (9/24/99),
Dr. Howell distributed a questionnaire (D. Howell e-mail, 9/24/99) to some specialists
in the state, soliciting assessment of a list of 22 criteria. A year later (D.
Howell e-mail, 9/18/00), he distributed an "Animal
Species Evaluation Worksheet" with ten criteria. Species are assigned
a score with respect to each criterion and the sum of these scores is used to
determine whether a species will be listed.
Further revisions
of the plant list have not been proposed; however, an amendment of the list
of animal species was
proposed
recently (October 2001). As with the 1998 proposed plant list, this amended
animal list is based on additional criteria, including "regional status, distribution
changes since 1930, estimated habitat changes in the next 10 years and population
trends" (Iowa DNR News, Natural Resource Commission, October 11, 2001). The
criteria used were those on the "Animal Species Evaluation Worksheet"
(see above), as well as "information and documentation of various experts"
(D. Howell e-mail, 3/6/02).
|
SOURCE
& CATEGORY |
IA
Adm. Code 1977 |
IA
Adm. Code 1984 |
IA
Adm. Code 1986 |
IA
Adm. Code 1988 |
IA
Adm. Code 1994 |
DNR
Prop. List 1998 |
| Endangered (E) |
100
|
123
|
123
|
140
|
64
|
16
|
| Threatened (T) |
52
|
56
|
56
|
58
|
89
|
93
|
| Special Concern (SC) |
|
|
28
|
227
|
167
|
|
| TOTAL E + T |
152
|
179
|
179
|
198
|
153
|
109
|
The number of listed species with legal protection (i.e., endangered and threatened) rose from approximately 150 in 1977 to nearly 200 in 1988, and then declined to 150 in 1994. One of the concerns regarding the list proposed in 1998 was that it would have further reduced the number of legally protected species to just over 100.
The law (as specified in the Iowa Acts and Joint Resolutions 1975) requires that the endangered species lists shall be reviewed at least every 2 years; however, reviews have been conducted irregularly and less frequently (1977, 1984, 1986, 1988 and 1994).
The purpose of the state lists should be to focus at the local level and provide protection for any rare species, even though some of these species may be more abundant or even common in other parts of the country. Clearly, that is the intent of the Iowa endangered species legislation, which is to protect species "determined to be endangered or threatened within the state" (Code of Iowa 1977). Balsam Fir (Abies balsamea (L.) Miller) is an example of a species that is rare in Iowa, but relatively widespread and common in parts of Minnesota and Wisconsin.
Considering how little we have left in Iowa, we should err on the side of caution. If there is any possibility that a species is rare, it should be given legal protection until proven otherwise; the onus should be on demonstrating that a species is not at risk, not that it is. Examples include such aquatics as one of the Duckweeds, Lemna perpusilla Torrey, and a Bur-reed, Sparganium androcladum (Engelm.) Morong. Both are known only from one or two sites, yet on the 1994 Iowa Code list, they are designated Special Concern, a category that gives no legal protection, and they were not on the 1998 DNR Proposed List.
Endangered species lists should have a sound scientific basis. In the past, herbarium specimens, literature citations, and sight records have been the sources for the Iowa lists. However, on