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Ohio Biological Survey Notes 7: 1-13, 2017. © Ohio Biological Survey, Inc. 


Quantifying Bee Diversity and Resource Use in the Appalachian Foothills near Marietta, Ohio 

MaLisa R. Spring*’^, Katy S. Lustofin^, Chia-Hua Lin^, Mary M. Gardiner^ and Dave McShaffrey^ 


’Department of Entomology, The Ohio State University, Wooster, OH 44691; -Department of Biology and Environmental Science, Marietta 
College, Marietta, OH 45750; ^Department of Evolution, Ecology and Organismal Biology, The Ohio State University, Columbus, OH 


43210 


Abstract: We surveyed bee ncliness, abundance, and diversity within Waslimgton County, Ohio Bees were collected 
at three sites within Washington County every two weeks from April to October 2013 using pan traps, vane traps, 
and hand collecting. A total of 2,753 bees were pinned and identified to genus, and when possible, species. A total 
of 35 genera of bees were collected representing over 130 species in five families. Of the species collected, 74 had 
fewer tlian 3 representatives. The most conmion genera were Andrena, Lasioglossiim, and Ceratina. Of the bees 
collected, 81 individuals, the majority of which were Andrena erigeniae (n=49) or Andrena violae (n=I2), had 
visible pollen loads. Andrena erigeniae was found to collect pollen mainly from Clay'tonia virginica. Andrena violae 
collected pollen from a variety of spring ephemerals in addition to violets, Overall, this research provides a baseline 
understanding of the current bee populations in southeastern Ohio. More work is needed m a larger variety of habitats 
to better understand the bee diversity and richness across southeastern Ohio. 


Introduction 

Victorian-era collection and identification of organisms seems to have gone out of style. However, habitat surveys are imperative 
for understanding changes in biodiversity over time. Local changes in richness and/or species diversity can only be determined 
if there is a baseline for comparison Worldwide, bees have been documented as m declme (Browm and Paxton, 2009). This 
includes decreases in both abundance and diversity and varies greatly depending on landscape changes (Burkle et al., 2013). As 
anthropogenic change continues, especially climate change, it is imperative to establish biodiversity baselines against which 
further surveys can be compared. 

Washington county is 1,657 km- and includes the small town (population 15,000) of Marietta (39.4154° N, 81 .4548° W). 
Marietta, Ohio, is rich in human history as the first capital of the Northwest Territory. However, the natural history of 
southeastern Ohio is sparse, especially involving bee species records. Therefore, this study set out to 1) determine the bee 
species richness and abundance in and around Marietta, Ohio, and 2) determine floral resource utilization of bees. 


Materials and Methods 

Sampling Sites. Three sites were chosen in Washington County: the Barbara A. Beiser Field Station, the Marietta College 
campus, and the Washington County Career Center From east to west, the Barbara A. Beiser Field station is ~12 kilometers 
from the Marietta College campus, which is ~8 kilometers from the Washington County Career Center. The Barbara A. Beiser 
Field Station was formally established in 2008 and transferred to co-management by Marietta College and Friends of the Lower 
Muskingum. It is 77 acres of forest, old field, and streamfront, most of which is on a slope. Each site had three transects of ~1 50 
meters (Figure 1 ). The transects at the field station were in old field habitat bordered by forest edge. The transects at the Marietta 
College campus were on turf grass next to a stream overrun with invasive and ornamental plants At the Washington County 
Career Center, one transect was on turf grass and tire other two transects were old field habitat bordered by forest edge. The 
final transect at the Washington County Career Center was a clearing for an oil well surrounded by many acres of dense forest. 

Bee Collection. Sampling consisted of bee bowls, hand-netting, and blue vane trapping. Bee bowls consisted of 96 ml souffle 
(Solo®) cups painted either fluorescent yellow, fluorescent blue, or left white (Guerra Paints) as per the standardized guidelines 
of the Handy Bee Manual (Droege, 2012). Ninety bee bowls were set every five meters along each 150 meter transect. The 
bowls were half-filled with soap solution (0.5% blue Dawn® dish soap and distilled water mixture) and left out for 24 hours. 
Sampling for the bee bowls took place approximately every 2 weeks from April 201 3 to mid-October 201 3 on non-rainy days. 


1 



Hand-collection and netting occurred three times: April 29th, July 3rd, and August 2nd. Hand-collection or netting involved 
timed walks of 5 minutes along the transects to catch any observed bee within 5 meters of the transect. Blue vane traps 
(SpringStar™) were incorporated in an attempt to catch larger bees that escape from smaller traps (Stephan and Rao, 2005). 
The vane traps were used starting at the end of August until the first frost in October. Only one vane trap was set per transect 
and they were deployed for the same duration as the bee bowls. As with the bee bowls, these were half-filled with the soapy 
water solution. 



Figure 1. Sampling sites: A) the Marietta College campus; B) the Washington County Career Center; C) the Barbara A. Beiser 
Field Station. 


Sample Preparation. Samples were stored in 70% ethanol. Bees were sorted from bycatch, washed, blown dry, and pinned 
as per recommendations from the Handy Bee Manual (Droege, 2012). Bees were identified to genus using Michener et al. 
(1994). Species identification was based largely on Discoverlife.org (Droege et al, 2013). Sam Droege (USGS Bee Inventory 
and Monitoring Lab) confirmed species-level identification of bees and identified all specimens in the genera Lasioglossum 
and Nomada. 

In addition to calculated species richness, the Simpson’s Diversity Index was used to calculate diversity (Simpson 1949). The 
modified Simpson’s Diversity Equation is as follows: 

D = 1 - ( X (m {ni - \)) I N{N-\)) 

Species accumulation curves for bee bowl samples were created in R (3.2.2) with package vegan (2.3-1). Samples were summed 
over the entire year and species complexes were removed from the analysis to get an estimate of species present. Simpson’s 
Diversity Index provides information about the diversity and evenness of the samples and range from 0 to 1, where 0 is a 100% 
probability of getting two specimens of the same species from a sample and 1 is a 0% probability of randomly selecting two 
specimens of the same species from a sample (Simpson 1949). 

Since most bees were collected in a soapy water solution, only bees with large, visible pollen loads were chosen for pollen 
analysis. Contamination from the collection method is possible; hence, only dominant pollen grains were identified to decrease 
the likelihood of identifying contaminants in the pollen masses. The pollen loads were gently scraped from the scopa with an 
insect pin and placed in labeled microcentrifuge tubes with 70% ethanol until they could be processed. Pollen slides were made 
using basic fuschin jelly to stain the grains (Kearns and Inouye, 1993) and then compared to a reference collection of pollen. 


Results 

Bees Collected. We collected 2,753 bees from the three locations sampled during 2013. A total of 28 bees were collected from 
vane traps, 147 were hand collected, and the remaining 2,578 were from bee bowls. Overall abundance was 995 at the Barbara 
A. Beiser Field Station, 760 at the Marietta College Campus, and 972 at the Washington County Career Center, with 26 bees 
collected elsewhere in Washington County. Five families of bees were collected: Apidae, Andrenidae, Colletidae, Halictidae, 
and Megachilidae. These pollinators belonged to 35 genera, and 130 species (Appendix 1). Of these 130 species, 74 had fewer 
than 3 representatives. The most common species were Andrena erigeniae, A. violae, Calliopsis andreniformis. Apis mellifera, 
Ceratina calcarata, C. mikmaqi, C. strenua, and Lasioglossum versatum. Eight species were state records (not previously 
reported) for Ohio: A. macro, Hylaeus leptocephalus, Nomada annulata, N. luteola, Melecta pacifica, Stelis nitida, L. gotham, 
and L. subviridatum. Only a small number of bees not native to the United States were found: A. wilkella (n=l), Anthidium 


2 


manicatum (n=5), An. oblongatum (n=41), Apis mellifera (n=146), H. leptocephalus (n=2), Megachile rotundata (n=35), Osmia 
cornifrons (n=3), and O. taurus (n=10). This study also found the first reported case of gynandromorphy (individual with both 
male and female body parts) in the bumble bee Bombus bimaculatus at the Barbara A. Reiser Field Station (Spring et af, 2015). 
This has only been reported in 113 bee species worldwide (Hinojosa-Diaz et af, 2012) with Michez et al. (2009) providing a 
comprehensive review of the condition. Very few of the bees were stylopized, with the authors only finding six specimens of 
Andrena with streps ipterans remaining in their abdomen (Spring et af, 2015). 

Species diversity estimates. The calculated bee diversity (D) for all sites was as follows: the Washington County Career Center 
(0.929), the Barbara A. Reiser Field Station (0.875), and the Marietta College Campus (0.957). 

A total of 2,434 specimens were used to create the species accumulation curves once species complexes were removed from 
the bee bowl data. Species accumulation curves were created for each site using chao, jackknife, and bootstrap (Table 1). The 
estimated species richness that could be collected via bee bowls is 172 (Chao), 172 (Jackknife 1), 194 (Jackknife2), and 147 
(Bootstrap) (Figure 2). 

Table 1. Species Accumulation Curve for bee bowl collection. 


Site 

Sampled species 
richness 

Chao 

Chao SE 

Jacki 

Jacki SE 

Jack 2 

Boot 

n 

Overall 

126 

172.22 

17.11 

172.22 

18.91 

194.97 

147.24 

9 

BFS 

52 

82.25 

14.75 

74 

16.93 

83.0 

62.22 

3 

MC 

77 

105.00 

11.83 

105 

19.80 

115.5 

90.22 

3 

WCCC 

77 

93.90 

7.46 

103 

19.87 

111.0 

89.67 

3 


3 4 5 6 7 6 9 



Size 


Figure 2. Species Accumulation Curve for bee bowl samples. 


Pollen analysis. A total of 81 bees collected had visible pollen loads. Of these 81 bees, 66 were from the genus Andrena. 
Furthermore, a majority of these bees were from QithQX Andrena erigeniae (n=50) or Andrena violae (n=12). Andrena erigeniae 
was found to collect mainly Claytonia virginica, a spring ephemeral common in Southeastern Ohio, but occasionally had other 
pollen in their loads including Taraxacum officinale, Caryophyllaceae, and Brassicaceae (Table 2). Andrena violae was found 
to have on average two dominant pollen types per load, but the types of pollen varied greatly by individual (Table 2). 


3 








Table 2. Pollen Loads 


Bee Species 

Average # of pollen types 
dominant per individual 

Pollen Type 

Andrena erigeniae 
(n=50) 

1.24 

Claytonia virginica. Taraxacum officinale, Caryophyllaceae, Brassicaceae 

Andrena perplexa 
(n=3) 

4 

Cornus spp., Viburnum spp., Carya spp. 

Andrena violae 
(n=12) 

2.16 

Rosaceae, Lamiaceae, Ranunculaceae, Lonicera spp., Oxalis stricta 

Halictus Hgatus 
(n=7) 

1.71 

Taraxacum officinale, Asteraceae 


Discussion 

There are only a few studies involving bees in Ohio, with most as part of ecological or agricultural studies and completed 
within the last decade (Arduser, 2010; Bernliardt et ah, 2008; Cusser and Goodell, 2013; Her and Goodell, 2014; Goodell et af, 
2010; Pardee and Philpott, 2014, Phillips and Gardiner 2015). Of the studies in the nearby states, there is a tendency to focus 
on an agricultural crop, such as apple orchards (Gardner and Ascher, 2006, Russo et af, 2015), sunflowers (Todd et af, 2016), 
or bluebeny^ (Tuell et af, 2009) among many otliers. Occasionally, nearby studies focus on specific habitat such as sand dunes 
(Grundel et af, 2011), powerline right-of-ways (Russell et af, 2005), or shale barrens (Kalhorn et af, 2003). Other states are 
working on bee diversity and richness estimates, but many states lack a defined species list (Tucker and Rehan, 2016). 

There is a dearth of species diversity surveys in Ohio. It is a large state, rich in biodiversity (thanks to the varietv^ of habitats), 
and is thus likely to host a wide diversity of bees. The most recently published bee diversity survey occurred in the northwestern 
portion of Ohio in the Oak Openings (Arduser,. 2010). This study took place on a nature preserve known for its biodiversity 
and unique habitat (Arduser, 2010). A direct comparison of diversity between these two studies is challenging because Arduser 
(2010) used hand-netting as the mam sampling method, whereas this study largely utilized bee bowls, which are known to 
attract a slightly different subset of pollinators. Moreover, this study took place tliroughout the entire flying season from end of 
frost to first frost in the fall. The sampling efToit for Arduser (2010) was mainly when the author had a chance to be in northern 
Ohio over a period of 3 years. Despite this discrepancy in sampling methods, Arduser (2010) found 116 species among 486 
individuals hand-collected from flowers, 

However, other than MitchelPs early work on bees across the United States, which only shows estimated distributions (Mitchell, 
1960, Mitchell, 1962), and the study in Northwestern Ohio by Arduser, bee diversity remains largely understudied in Ohio. 
This is the first published year-long survey of bee diversity in soutlieastern Ohio known to the authors. We found a total of 130 
bee species, which is similar in number, but not composition, to other bee diversity studies (Arduser, 2010; Giles and Ascher, 
2006; Grundel et af, 201 1 ). We found a total of eight state records of bee species not previously reported in Ohio (Sam Droege, 
pers. comm). Of these records, one was a newly split species group (I. gotham) (Gibbs, 2011) or invasive (H. leptocephalus). 
Two records are of species not reported in many collections (A. macro and L. siibviridatum); thus, they are rare in general. The 
remainder are parasites of other bees {N. ammlata, N. luteoloa, Melecta pacifica, and S. nitida). This number of state records 
could be partly due to the habitat; the Appalachian foothills are still understudied for their bee diversity, and most research 
involving bees occurs in the central and northern region of the state. 

Species diversity was calculated using the reciprocal Simpson’s Diversity Index. With tins equation, a larger value (between 
0-1) on the Simpson’s Diversity Index indicates a greater likelihood of randomly selecting two different species when selecting 
two specimens. A larger value can therefore be interpreted as a higher-diversity assemblage. All three sites had high index 
values (>0.85), which would imply diverse assemblages and good biodiversity of the overall area Moreover, the species 
estimates for just bowl collection of the area range from 147-194 species, whereas we only collected a total of 126 species 
with bee bowls. This implies that subsequent years of sampling with bee bowls should still find more species. Importantly, 
this calculation did not take into account alternative sampling methods, which are known to collect a different subset of the 
biodiversity in bees. Thus, the authors recommend additional effort in Washington County focusing on vane traps and hand- 
collection to get a better idea of bee richness. 


4 














Pollen loads. Of the 2,753 bees collected, few had visible pollen loads remaining once they got back to the lab. This could be 
partly due to the pollen packing methods of different bee species. Some species mix pollen with nectar to get the mass to stay 
attached to the scopa, whereas others just brush the pollen onto their scopa. Of the bees collected with visible pollen loads, most 
were in the genus Andrena. Andrena erigeniae is often stated as a pollen specialist on Claytonia virginica (Reese and Barrows, 
1980). All of our specimens were found to be collecting C. virginica pollen, though they did occasionally have large quantities 
of other pollens present. 

Many articles, without referencing sources, state that A. violae only pollinates violets (Motton, 1986; Giles and Ascher, 2006). 
In our case, A. violae is found to collect pollen from a variety of sources, rarely having similar pollen loads. Older literature 
shows that A. violae is documented on many spring ephemerals in addition to violets (Robertson 1929; Mitchell 1960), which 
is more in line with our data. 


Future Research 

The authors recommend that the study be repeated in a few years with more hand-netting to collect more species. Increased 
hand-collection has the potential to find more species that are unlikely to visit bee bowls. Furthermore, collection at additional 
sites with a wider variety of habitats and fioral resources is recommended to get a better idea of the diversity present in and 
around the historic area of Marietta, Ohio. 


Acknowledgements 

We would like to thank Sam Droege from the USGS Bee Inventory and Monitoring Lab for his help with confirmations of 
IDs and species identification of the Lasioglossum and Nomada. We would also like to thank Karen Goodell for access to her 
reference collection of Ohio bees in the spring of 2014. Thanks also go to the following undergraduates at Marietta College 
who assisted with the 3:00 a.m. set-up time for bee bowls and vane traps or hand-collecting during the day: Rachel Shoop, 
Anna Cooper, Tristine Toves, and Rachel Stahl. Furthermore, we would like to thank the Marietta College Investigative Studies 
program and the Biology and Environmental Science Department for funding this project, and the Investigative Studies Travel 
grant for funding travel to both the Association for Southeastern Biologists meeting and the International Conference for 
Pollinator Biology, Health, and Policy. Thanks for diversity index calculation and interpretation goes to Katherine Todd and 
Bryan Zake. A synoptic collection of this research is housed at the Museum of Biological Diversity at The Ohio State University. 


Appendix 1. Species list and abundance of individuals. 


Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

CO 

1- 

(J 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Agapostemon 

virescens 

29 

1 

1 

0 

2 

5 

4 

10 

19 

5 

3 

0 

8 

0 

Andrena 

Barbara 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Andrena 

harhilabris 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Andrena 

bisalicis 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Andrena 

bradleyi 

1 

0 

0 

0 

0 

0 

0 

1 

1 

0 

0 

0 

0 

0 

Andrena 

brevipalpis 

3 

0 

0 

1 

1 

1 

0 

1 

2 

0 

0 

0 

0 

0 

Andrena 

carlini 

3 

0 

0 

2 

2 

0 

0 

0 

0 

1 

0 

0 

1 

0 


5 

















Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Andrena 

commoda 

1 

0 

0 

1 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Andrena 

cressonii 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Andrena 

cressonii 

cressonii 

5 

0 

1 

0 

1 

0 

1 

0 

1 

0 

0 

1 

1 

2 

Andrena 

distans 

3 

1 

0 

0 

1 

0 

1 

1 

2 

0 

0 

0 

0 

0 

Andrena 

erigeniae 

323 

42 

94 

96 

232 

10 

16 

21 

47 

6 

10 

28 

44 

0 

Andrena 

gardineri 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Andrena 

illini 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

Andrena 

imitatrix 

2 

0 

0 

0 

0 

0 

1 

1 

2 

0 

0 

0 

0 

0 

Andrena 

macra 

3 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

2 

3 

0 

Andrena 

miserabilis 

2 

0 

0 

0 

0 

1 

1 

0 

2 

0 

0 

0 

0 

0 

Andrena 

nasonii 

3 

0 

0 

1 

1 

0 

0 

0 

0 

1 

0 

1 

2 

0 

Andrena 

nubecula 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Andrena 

perplexa 

40 

0 

6 

0 

6 

8 

10 

4 

22 

4 

7 

1 

12 

0 

Andrena 

placata 

2 

0 

1 

0 

1 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Andrena 

pruni 

2 

0 

2 

0 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Andrena 

robertsonii 

2 

0 

0 

0 

0 

0 

0 

1 

1 

0 

1 

0 

1 

0 

Andrena 

sayi 

2 

0 

2 

0 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Andrena 

simplex 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Andrena 

sp. 

4 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

3 

4 

0 

Andrena 

vicina 

3 

0 

0 

0 

0 

1 

1 

1 

3 

0 

0 

0 

0 

0 

Andrena 

violae 

266 

59 

77 

44 

180 

12 

14 

18 

44 

5 

21 

16 

42 

0 

Andrena 

wheeleri 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 


6 

















Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Andrena 

wilkella 

1 

0 

1 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Anthidiellum 

notatum 

notatum 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Anthidium 

manicatum 

6 

0 

0 

0 

0 

2 

0 

1 

3 

0 

2 

0 

2 

1 

Anthidium 

oblongatum 

40 

0 

0 

0 

0 

7 

13 

5 

25 

0 

11 

3 

14 

1 

Anthophora 

terminalis 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Apis 

mellifera 

147 

5 

10 

4 

19 

21 

41 

27 

89 

15 

11 

10 

36 

3 

Augochlora 

pura 

49 

6 

22 

2 

30 

2 

2 

3 

7 

2 

7 

3 

12 

0 

Augochlorella 

aurata 

16 

0 

0 

0 

0 

0 

0 

1 

1 

1 

7 

7 

15 

0 

Augochloropsis 

metallica 

7 

0 

1 

0 

1 

1 

1 

1 

3 

1 

1 

1 

3 

0 

Bombus 

auricomus 

2 

0 

0 

0 

0 

0 

0 

1 

1 

0 

0 

0 

0 

1 

Bombus 

bimaculatus 

15 

6 

1 

0 

7 

2 

1 

2 

5 

0 

1 

1 

2 

1 

Bombus 

griseocollis 

4 

0 

0 

0 

0 

0 

4 

0 

4 

0 

0 

0 

0 

0 

Bombus 

impatiens 

20 

0 

0 

0 

0 

7 

3 

2 

12 

0 

3 

3 

6 

2 

Bombus 

perplexus 

3 

1 

0 

0 

1 

0 

1 

1 

2 

0 

0 

0 

0 

0 

Bombus 

vagans 

2 

0 

0 

0 

0 

1 

1 

0 

2 

0 

0 

0 

0 

0 

Calliopsis 

andreniformis 

95 

2 

2 

0 

4 

0 

3 

3 

6 

0 

16 

69 

85 

0 

Ceratina 

CClicClTCltCl 

169 

7 

64 

15 

86 

38 

5 

5 

48 

11 

5 

19 

35 

0 

Ceratina 

da^la 

38 

2 

7 

8 

17 

3 

0 

1 

4 

1 

7 

9 

17 

0 

Ceratina 

mikmaqi 

97 

5 

26 

21 

52 

4 

0 

1 

5 

3 

14 

23 

40 

0 

Ceratina 

sp. 

5 

0 

3 

0 

3 

1 

0 

0 

1 

0 

0 

1 

1 

0 

Ceratina 

strenua 

396 

7 

115 

27 

149 

26 

17 

23 

66 

22 

25 

134 

181 

0 

Chelostoma 

philadelphi 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 


7 

















Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Coelioxys 

sayi 

1 

0 

0 

0 

0 

0 

0 

1 

1 

0 

0 

0 

0 

0 

Coelioxys sayi/ 
octodenata 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Colletes 

inaequalis 

3 

0 

1 

0 

1 

0 

0 

1 

1 

0 

0 

0 

0 

1 

Colletes 

simulans 

1 

0 

0 

1 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Eucera 

atriventris 

15 

3 

0 

1 

4 

2 

1 

3 

6 

2 

0 

3 

5 

0 

Eucera 

dubitata 

3 

0 

2 

0 

2 

0 

0 

1 

1 

0 

0 

0 

0 

0 

Eucera 

hamata 

3 

0 

1 

0 

1 

0 

0 

1 

1 

1 

0 

0 

1 

0 

Eucera 

sp. 

1 

0 

0 

1 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Halictus 

confusus 

23 

0 

0 

0 

0 

7 

10 

4 

21 

0 

0 

0 

0 

2 

Halictus 

ligatus 

76 

2 

7 

1 

10 

11 

3 

6 

20 

8 

15 

23 

46 

0 

Halictus 

rubicundus 

9 

1 

2 

0 

3 

1 

1 

0 

2 

2 

2 

0 

4 

0 

Halictus 

sp. 

2 

0 

0 

0 

0 

2 

0 

0 

2 

0 

0 

0 

0 

0 

Heriades 

leavitti/ 

variolosa 

2 

0 

2 

0 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Holcopasites 

calliopsidis 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

2 

2 

0 

Hoplitis 

pilosifrons 

8 

0 

0 

0 

0 

1 

0 

0 

1 

0 

2 

5 

7 

0 

Hoplitis 

producta 

22 

4 

3 

4 

11 

6 

0 

2 

8 

0 

2 

1 

3 

0 

Hoplitis 

spoliata 

1 

0 

0 

0 

0 

0 

0 

1 

1 

0 

0 

0 

0 

0 

Hylaeus 

affinis/ 

modestus 

27 

3 

5 

2 

10 

4 

2 

1 

7 

0 

6 

4 

10 

0 

Hylaeus 

hyalinatus 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Hylaeus 

leptocephalus 

2 

0 

0 

0 

0 

2 

0 

0 

2 

0 

0 

0 

0 

0 

Hylaeus 

mesillae 

3 

0 

0 

0 

0 

1 

1 

0 

2 

0 

0 

1 

1 

0 

Hylaeus 

sp. 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 


8 

















Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Lasioglossum 

admirandum 

2 

0 

0 

0 

0 

2 

0 

0 

2 

0 

0 

0 

0 

0 

Lasioglossum 

bruneri 

4 

0 

0 

0 

0 

2 

2 

0 

4 

0 

0 

0 

0 

0 

Lasioglossum 

cattallac 

2 

0 

0 

0 

0 

0 

1 

0 

1 

0 

1 

0 

1 

0 

Lasioglossum 

coriaceum 

6 

0 

0 

0 

0 

2 

0 

1 

3 

0 

0 

3 

3 

0 

Lasioglossum 

cressonii 

5 

2 

0 

1 

3 

0 

0 

0 

0 

0 

1 

1 

2 

0 

Lasioglossum 

ephialtum 

6 

0 

0 

0 

0 

4 

1 

0 

5 

1 

0 

0 

1 

0 

Lasioglossum 

foxii 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Lasioglossum 

fuscipenne 

2 

0 

1 

0 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

Lasioglossum 

gotham 

10 

1 

0 

0 

1 

1 

4 

1 

6 

1 

0 

2 

3 

0 

Lasioglossum 

hitchensi 

52 

1 

5 

1 

7 

10 

11 

10 

31 

3 

5 

6 

14 

0 

Lasioglossum 

imitatum 

21 

0 

1 

0 

1 

9 

6 

5 

20 

0 

0 

0 

0 

0 

Lasioglossum 

katherineae 

1 

0 

0 

0 

0 

0 

1 

0 

1 

0 

0 

0 

0 

0 

Lasioglossum 

obscurum 

3 

0 

0 

0 

0 

2 

1 

0 

3 

0 

0 

0 

0 

0 

Lasioglossum 

para- 

admirandum 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Lasioglossum 

quebecense 

3 

0 

1 

0 

1 

0 

0 

0 

0 

1 

0 

1 

2 

0 

Lasioglossum 

sp. 

76 

3 

9 

2 

14 

20 

6 

7 

33 

5 

11 

9 

25 

4 

Lasioglossum 

subviridatum 

10 

0 

3 

1 

4 

1 

0 

0 

1 

2 

2 

1 

5 

0 

Lasioglossum 

tegulare 

3 

0 

0 

0 

0 

1 

0 

1 

2 

0 

0 

1 

1 

0 

Lasioglossum 

truncatum 

2 

0 

0 

0 

0 

0 

0 

1 

1 

0 

0 

1 

1 

0 

Lasioglossum 

versans 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Lasioglossum 

versatum 

202 

4 

34 

12 

50 

8 

9 

1 

18 

34 

49 

51 

134 

0 

Megachile 

brevis 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

2 

0 


9 

















Species 

Total 

BPS T1 

C\l 

1- 

co 

LL 

DO 

BPS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Megachile 

campanulae 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

2 

0 

Megachile 

centuncularis 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Megachile 
inimica sayi 

1 

0 

0 

1 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Megachile 

mendica 

6 

0 

0 

0 

0 

0 

2 

2 

4 

1 

1 

0 

2 

0 

Megachile 

montivaga 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Megachile 

petulans 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Megachile 

rotundata 

37 

0 

0 

0 

0 

13 

15 

5 

33 

1 

0 

2 

3 

1 

Megachile 

sp. 

2 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

2 

0 

Melecta 

pacifica 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Melissodes 

himaculatus 

15 

2 

2 

0 

4 

3 

2 

3 

8 

1 

0 

1 

2 

1 

Melissodes 

coloradensis 

1 

0 

1 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Melissodes 

denticulata 

13 

2 

6 

0 

8 

0 

0 

0 

0 

1 

3 

1 

5 

0 

Melissodes 

desponsa 

7 

0 

1 

1 

2 

0 

1 

0 

1 

1 

2 

1 

4 

0 

Melissodes 

druriella 

2 

0 

0 

0 

0 

0 

1 

0 

1 

0 

1 

0 

1 

0 

Melissodes 

sp. 

2 

0 

0 

2 

2 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Melitoma 

taurea 

15 

4 

6 

0 

10 

1 

0 

2 

3 

1 

0 

1 

2 

0 

Nomada 

(Bidentate) 

15 

0 

2 

0 

2 

1 

3 

1 

5 

4 

1 

3 

8 

0 

Nomada 

annulata 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Nomada 

articulata 

4 

0 

0 

0 

0 

3 

0 

1 

4 

0 

0 

0 

0 

0 

Nomada 

cressonii 

1 

0 

0 

0 

0 

1 

0 

0 

1 

0 

0 

0 

0 

0 

Nomada 

denticulata 

2 

1 

0 

0 

1 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Nomada 

depressa 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Nomada 

fervida 

1 

0 

1 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 


10 

















Species 

Total 

BFS T1 

C\l 

1- 

co 

LL 

DO 

BFS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Nomada 

imbricata 

18 

0 

2 

0 

2 

0 

2 

0 

2 

3 

4 

7 

14 

0 

Nomada 

luteola 

1 

0 

0 

0 

0 

0 

0 

0 

0 

1 

0 

0 

1 

0 

Nomada 

luteoloides 

4 

0 

0 

0 

0 

0 

1 

0 

1 

1 

0 

2 

3 

0 

Nomada 

parva 

3 

0 

0 

0 

0 

0 

0 

1 

1 

1 

0 

1 

2 

0 

Nomada 

pygmaea 

7 

0 

1 

0 

1 

1 

0 

1 

2 

3 

0 

1 

4 

0 

Nomada 

sp. 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Osmia 

atriventris 

7 

0 

0 

0 

0 

2 

1 

1 

4 

0 

2 

1 

3 

0 

Osmia 

hucephala 

17 

6 

1 

2 

9 

2 

1 

0 

3 

0 

1 

4 

5 

0 

Osmia 

caerulescens/ 

cordata 

5 

0 

0 

0 

0 

2 

0 

0 

2 

2 

0 

1 

3 

0 

Osmia 

collinsiae 

3 

0 

0 

0 

0 

0 

0 

0 

0 

2 

0 

1 

3 

0 

Osmia 

cordata 

18 

0 

0 

1 

1 

10 

1 

2 

13 

2 

1 

1 

4 

0 

Osmia 

cornifrons 

3 

0 

0 

0 

0 

0 

0 

1 

1 

1 

0 

1 

2 

0 

Osmia 

distincta 

4 

0 

0 

0 

0 

0 

0 

1 

1 

1 

2 

0 

3 

0 

Osmia 

georgica 

15 

2 

2 

2 

6 

3 

1 

0 

4 

2 

0 

3 

5 

0 

Osmia 

inspergens 

1 

0 

0 

0 

0 

0 

1 

0 

1 

0 

0 

0 

0 

0 

Osmia 

pumila 

9 

0 

2 

1 

3 

0 

0 

0 

0 

1 

2 

3 

6 

0 

Osmia 

sp. 

21 

1 

1 

0 

2 

7 

0 

1 

8 

5 

3 

3 

11 

0 

Osmia 

subfasciata 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Osmia 

taurus 

12 

1 

0 

1 

2 

0 

1 

2 

3 

3 

0 

2 

5 

2 

Panurginus 

potentillae 

3 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

3 

3 

0 

Peponapis 

pruinosa 

4 

0 

0 

0 

0 

1 

1 

0 

2 

0 

1 

1 

2 

0 

Ptilothrix 

bombiformis 

11 

0 

0 

0 

0 

2 

4 

2 

8 

1 

1 

1 

3 

0 


11 

















Species 

Total 

BPS T1 

C\l 

1- 

co 

LL 

DO 

BPS T3 

BFS Total 

MCT1 

MCT2 

MCT3 

MC Total 

WCCC T1 

WCCC T2 

WCCC T3 

WCCC 

Total 

Other 

Sites 

Sphecodes 

coronus 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

0 

Stelis 

lateralis 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Stelis 

nitida 

1 

1 

0 

0 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

Triepeolus 

cressonii? 

1 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

0 

1 

0 

Xylocopa 

virginica 

4 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

1 

1 

3 

SUM 

2753 




995 




760 




972 

26 


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Brown, J. F., and Paxton, R. J. 2009. The conservation of bees: a global perspective. Apidologie 40: 410-416. 

Burkle, L. A., Marlin, J. C., and Knight, T. M. 2013. Plant-pollinator interactions over 120 years: loss of species, co- 
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Cusser, S., and Goodell, K. 2013. Diversity and distribution of floral resources influence the restoration of plant-pollinator 
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Droege, S. 2012. The very handy manual: how to catch and identify bees and manage a collection. USGS Native Bee Inventory 
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Droege, S., Jean, R., and Orr, M. 2013. Discover Eife ID nature guide (draft): bee genera of Eastern North America 
(Hymenoptera: Apoidea: Anthophila). Available from http://www.discoverlife.org/mp/20q?search=Apoidea 

Her, A. M., and Goodell, K. 2014. Relative floral density of an invasive plant affects pollinator foraging behavior on a native 
plant. Journal of Pollination Ecology 13: 173-183. 

Gardner, K. E., and Ascher, J. S. 2006. Notes on the native bee pollinators in New York apple orchards. Journal of New York 
Entomological Society 114: 86-91. 

Gibbs, J. 2011. Revision of the metallic Lasioglossum (Dialictus) of eastern North America (Hymenoptera: Halictidae: 
Halictini). Zootaxa 3073: 1-216. 

Giles, V., and Ascher, J. S. 2006. A survey of the bees of the Black Rock Forest Preserve, New York. Journal of Hymenoptera 
Research 15: 208-231. 

Goodell, K., McKinney, A. M., and Lin, C. H. 2010. Pollen limitation and local habitat-dependent pollinator interactions in 
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Grundel, R., Jean, R. P., Frohnapple, K. J., Gibbs, J., Glowacki, G. A., and Pavlovic, N. B. 2011. A survey of bees 
(Hymenoptera: Apoidea) of the Indiana Dunes and Northwest Indiana, USA. Journal of the Kansas Entomological Society 
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Hinojosa-Diaz, 1. A., Gonzalez, V. H., Ayala, R., Merida, J., Sagot, P., and Engel, M. S. 2012. New orchid and leaf-cutter 
bee gynandromorphs, with an updated review (Hymenoptera: Apoidea). Zoosytematics and Evolution 88(2): 205-214. 

Kalhorn, K. D., Barrows, E. M., and LaBerge, W. E. 2003. Bee (Hymenoptera: Apoidea: Apiformes) diversity in an 
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Kearns, C. A., and Inonye, D. W. 1993. Techniques for pollination biologists. University Press of Colorado, Boulder, CO. 
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Michener, C. D., McGinley, R. J., and Danforth, B. N. 1994. The bee genera of North and Central America (Hymenoptera: 
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13 



Ohio Biological Survey Notes 7: 14-16, 2017. © Ohio Biological Survey, Inc. 


A Bilateral Gynandromorph Northern Cardinal from South Bass Island 

Andrew W. Jones’ and H. Thomas Bartlett 

Department of Ornithology, Cleveland Museum of Natural History, 1 Wade Oval Drive - University Circle, Cleveland, OH 44106; 
'corresponding author; ajones@cmnh.org 


Abstract: We report on a Northern Cardinal from South Bass Island, in the western basin of Lake Erie, which showed 
male plumage characteristics on the right side and female plumage characteristics on the left side. This condition, 
termed bilateral gynandromorph ism, is rare among wild birds, and there are few (<1 00) preseiwed specimens available 
for research. This bird had a slightly enlarged ovary on the left side and a small and probably non-functional testis on 
the right side. The plumage was fairly well demarcated between the two sides, but the female side was interspersed 
with red feathers and the male side was interspersed with brown. A recent study of gynandromorph domestic chickens 
provides a likely pathway for the origin and appearance of these Northern Cardinals. We suggest that a recent spate 
of records is probably due to increasing numbers of observant birdwatchers as well as the ubiquity of digital cameras. 

Keywords: Cardinalis cardinalis, bilateral gynandromorph, plumage 


Introduction 

Gynandromorphy is a rarely encountered condition in which an organism displays a combination of male and female 
characteristics This condition may be bilateral, with one half of tire organism phenotypically male and the other half 
phenotypically female, often with a clear line separating the two sides. Individuals with this condition are known across 
multiple classes of Metazoans, and individuals with this condition have been documented in both captive fowl as well as wild 
birds (Kumerloeve 1954). Kumerloeve (1954) conducted a review of this condition and the mechanisms that may underlie it, 
and documented several dozen instances m wild birds. Patten (1993) updated this review, and several additional records have 
been published since then (e.g., DaCosta et al. 2007, Peer and Motz 2014). No formal systematic review of gynandromorphism 
records has been conducted, but there are certainly more than fift\^ published examples as of this writing. Wild birds with 
gynandromorphism have been documented in many taxonomic orders and families across Aves, though there are multiple 
reports of gynandromorphy in Eurasian Bullfinch {Pyrrhula pytrhula) and Evenmg Grosbeak {Coccothraustes vesperthms), 
two members of the Fringillidae family. Published records are an underrepresentation of tlie prevalence of this condition, 
as any species without obvious size or plumage-related sex differences could only be documented through dissection by a 
knowledgeable museum specimen preparator. 

In this article, we document a bilateral gynandromorph Northern Cardinal {Cardinalis cardinalis) from South Bass Island, 
Ottawa County, Ohio. 


Specimen Data 

Bartlett operates a banding station for several weeks every spring and fall on private property on the east end of South Bass 
Island, in the western basin of Lake Erie (Ottawa County, Oliio, USA: 41.66239'^N, 82.79624‘^W). While banding on 01 May 
2011, Bartlett and Jones encountered an unusual Northern Cardinal. The bird was initially identified as a female with an 
unusual molt pattern; Bartlett has encountered other female Northern Cardinals with excessive red presumably due to age and/ 
or eccentric molt. Further examination demonstrated that the red coloration was primarily restricted to the right side of the bird, 
and there was a fairly sharp color demarcation down the middle of the bird’s body. Jones made the decision to collect the bird, 
and the specimen was transferred to the ornithology research collection at the Cleveland Museum of Natural History. 

Jones prepared the bird specimen (collector number AWJ 596, and cataloged as CMNH 74623), The bird weighed 43. 1 g. There 
was a little molt on this bird, wliich is unusual for a Northern Cardinal in May (like most songbirds, they ty'pically do not molt 
during the early part of the breeding season); several feathers on the right breast were being replaced, the left innermost tail 


14 



feather (Rl) was being replaced and was about 80% grown, and the right innermost tail feather was missing. There was no 
cloacal protuberance nor brood patch, suggesting that this bird was unpaired. The wing chord of both wings was 91mm, which 
is within the size range of both male and female Northern Cardinals (Pyle 1997). During dissection, Jones found an ovary on 
the bird’s left side that measured 8 x 5 mm, with the largest ovum 2 mm in diameter, and with a slightly enlarged oviduct. On 
the right side, an apparent testis was found, but it was small (for this time of year; 2 x l mm) and black in color, indicating that 
it may not have been functional. 

The bird’s plumage differs between the left and right sides most sharply on the ventral side, with a sharp demarcation on 
the breast, belly, and undertail coverts (Figure 1). The right side is red, though not nearly as bright red as a typical male, and 
interspersed with several partly or completely brown feathers. The left side is the same color of brown as a typical female, 
interspersed with a few red feathers. The head plumage is consistent with a female: dusl<y rather than solid black feathers 
surrounding the bill, brownish- gray feathers with a red crest, but with scattered red feathers on the face on the right side. The 
back is also consistent with a female, with brownish-gray feathers across the nape, mantle, scapulars, and uppertail coverts, but 
interspersed with some red feathers on the right side. The left tail feathers have dusky tips on the underside and dusky outer 
margins; the right tail feathers are almost entirely red. 



Figure 1. Ventral view of a specimen (CMNH 74623) of a bilateral gynandromorph Northern Cardinal. The red plumage on 
the bird’s right side is not as fully red as a typical male Northern Cardinal. The bird is not perfectly bilaterally symmetrical; 
there are female-like feathers on the male side, and male-like feathers on the female side. 


Discussion 

This Northern Cardinal specimen is the third record of gynandromorphy in this species in the peer-reviewed literature. Laskey 
(1954) banded one in central Tennessee. Like our report, it was male on the right side, but she noted that hers had brilliant red 
feathers rather than the dull red we observed. Her record was otherwise similar to ours, with a sharp demarcation line on the 
underside, and a female-like head. Peer and Motz (2014) observed a gynandromorph which was male on the left side. It had 
brilliant red feathers on the left side. Despite being observed throughout the breeding season, the bird did not pair with another 
bird. Playback experiments were conducted, and the bird changed its posture and awareness in response to the song of another 
Northern Cardinal, but did not sing. Other Northern Cardinals did not show any noticeable behavior such as aggression towards 
the gynandromorph. 

We are also aware of several putative records of gynandromorph Northern Cardinals that have been circulated on various 
internet websites, with photographs. Some of these individuals appear to be gray rather than brown over part of the body, 
suggesting a pigment abnormality rather than gynandromorphism. However, we have also seen photographs of a bird from 
Virginia that closely resembles our bird (https://www.flickr.com/photos/birdsofvirginia/3370349942/). A newsletter article 
(Bohlen 2006) reported on two records from Illinois. One was accompanied by a series of photographs and indicated that the 


15 



bird was seen singing, was seen carrying nesting material, and was socially associating with a female. Overall, there have been 
perhaps six records of Northern Cardinal gynandromorphs, and five of these have been in the last two decades. We attribute 
this to an increase in the number of active birdwatchers, increasing access to digital cameras and cell phones to document these 
birds, and an improved ability to communicate these sightings through the Internet. 

Including the present study, four of the five verifiable bilateral gynandromorph Northern Cardinals were male-plumaged on 
tire right side. This is the typical condition for bilateral g}mandromorphs in other birds as well; in birds, the females typically 
only develop an ovary on the left side (Kumerloeve 1954). However, some gynandromorphs have an ovary on the left and 
a testis on the right, yet the plumage sides are reversed from the gonads (e.g., DaCosta et al. 2007). Most of these Northern 
Cardinal records include scattered red feathers on the female side, and brown feathers on the male side. Plumage differences 
between the two sides are often imperfect in gynandromorphs, and this may be related to the mechanism causing the condition. 
The genetic basis underlying gynandromorphism is not completely understood. Graves (1996) reviewed variations on the 
symmetry of gynandromorphs and indicated that there may be multiple pathways to this condition. Zhao et al. (2010) examined 
three gynandromorph ic domestic chickens { Gall us gal I us) from a genetic and cellular perspective and demonstrated that those 
individuals were male-female chimaeras; some cells have ZW sex cliromosomes typical of females, and other cells have ZZ 
sex chromosomes typical of males. Most of the cells on tlie male-plumaged side were ZZ, and most of the cells on the female- 
plumaged side were ZW. As a result of the incomplete sorting of male and female cells between the two sides, the chickens 
they studied had featliers on each side that corresponded to the opposite sex. This mechanism likely e.xplains why the Northern 
Cardinals in this and other reports tend to have imperfect plumage symmetry'. The gynandromorphs studied by Zhao et al. 
(2010) probably result from an error in oogenesis in the mother of the gynandromorph, resulting into two nuclei in the fertilized 
ovary. It is unclear if this explanation is universal to all gynandromorphs, and we encourage further collection and study of 
wild and domestic birds with this condition. We suggest that researchers should preseiwe extensive tissue samples, including 
freezing or fomialin preserving of the entire body and sectioning the gonads to ascertain their functionality. 


Acknowledgments 

We thank Paula Bartlett, John Lortz, and Lisa Brohl for their help with banding activities, and Mark and Barb Barnhill for 
permission to study birds on their property. Mist-netting and banding is carried out under permits to H. Thomas Bartlett (Federal 
Permit 21624 and Ohio State Permits 17-177 and 17-82), and specimen collection is carried out under permits to Andrew W 
Jones (Federal Fish and Wildlife Permit MB12477201 and Ohio Wild Animal Permit 14-205). 


Literature Cited 

Bohlen, H. D. 2006. Illinois sightings of bilateral gynandromorphism in birds. The Living Museum 68:15-16. 

DaCosta, J. M., Spellman, G. M., and Klicka, J. 2007. Bilateral gynandromorphy in a White-ruffed Manakin (Corapipo 
ahem). The Wilson Journal of Ornithology 1 19:289-291 . 

Graves, G. R. 1996. Comments on a probable gynandromorphic Black-Throated Blue Warbler. Wilson Bulletin 108:178-180. 
Kumerloeve, H. 1954. On gynandromorphism in birds. Emu 54:71-72. 

Laskey, A. R. Bilateral gynandrism in a Cardinal and a Rufous-Sided Towhee. The Auk 86:760. 

Patten, M. A. 1993. A probable bilateral gynandromorphic Black-Throated Blue Warbler. Wilson Bulletin 105:695-698. 

Peer, B. D. and Motz, R. W. 2014. Observations of a bilateral gynandromorph Northern Cardinal {Cardinalis cardinalis). The 
Wilson JoLimal of Ornithology 126.778-781. 

Pyle, P. 1997. Identification guide to North American birds: Part I. Slate Creek Press, Bolinas, California. 

Zhao, D., McBride, D., Nandi, S., McQueen, H. A., McGrew, M. J., Hocking, P. M., Lewis, P. D., Sang, H. M., and 
Clinton. M. 2010. Somatic sex identity^ is cell autonomous in the chicken. Nature 464: 237-243. 


16 



Ohio Biological Survey Notes 7: 16-20, 2017. © Ohio Biological Survey, Inc. 


A Survey of the Turtles of Mentor Marsh, Lake County, Ohio 

Timothy O. Matson'*, Dana Smith-, and Samantha Skerlec^ 

’Department of Vertebrate Zoology, Cleveland Museum of Natural History, Cleveland , OH 44106; -Biology Department, Denison 
University, Granville, OH 43023; ^Biology Department, John Canoll University, University Heights, OH 44118; * corresponding author: 
tmatson@cmnh.org 


Abstract: Turtle trapping records and observations from 1979-2016 were compiled to survey the turtles of Mentor 
Marsh, Lake County, Ohio. Six species of turtles were previously known to occur in Mentor Marsh prior to 2016. 
Two species of turtles known from the marsh since the 1930s, Emydoidea blcmdingii and Clenimys gutatta, were not 
observed or trapped. Sternothenis odoratus (Eastern Musk Turtle) was recorded for the first time from Mentor Marsh 
and is a new Grand River drainage system record. 


Keywords: Mentor Marsh, salt intrusions, Emydoidea blandingii, Clemmys gutatta, Sternotherus odoratus 


Introduction 

Mentor Marsh is a large coastal wetland positioned at the mouth of the old Grand River at Lake Erie in Lake County, Ohio. It 
became a national natural landmark in 1966 and was dedicated as Ohio’s first state nature preserve in 1971. Ownership of the 
marshlands is shared by the state of Ohio, the City of Mentor, the Cleveland Museum of Natural History, and by private land 
owners. The marsh occupies the old Grand River channel and its floodplain (Bolsenga and Herdendorf 1993) and includes 
nearly 868 acres (361 hectares, Fineran 2003) on the Lake Erie Plains (Brockman 2002, White 1980). The marsh is about 6.9 
km (4.3 miles) long and approaches 0.8 km (0.5 miles) in width at the widest points and has a perimeter of approximately 20 km 
(12.5 miles). Two tributary streams flow into the marsh from the south' Marsh Creek enters into the western basin, and Black 
Brook enters into the eastern basin (Figure 1). 

The Grand River formerly meandered northward over the lake plain of low relief to within 0.5 km of Lake Erie before turning 
westward paralleling the shoreline of the lake. It entered Lake Erie at what is now Mentor Harbor (also referred to as Mentor 
Marina/Mentor Lagoons ) At some time following the formation of modem Lake Erie (approximately 4000 years BCE) and 
before 1 796 when the marsh w^as first surveyed (Holley 1 796; Pease 1 796), an event occurred where the river breached through 
its north bank and connected with the lake at Fairport Harbor. Water flow to the w'est of the cut-off was diminished, and over 
time, a diverse mosaic of wetland communities became established in the relict Grand River channel while swamp forests 
developed upon its flood plain (Bolsenga and Herdendorf 1993). 

Available riverine and wetland habitats have been conducive to support several species of turtles. Records and distribution 
maps of Conant (1951 ) and Zemko (1974) included four species of turtles for Mentor Marsh, The records included Chelydra 
serpentina (Snapping Turtle), Chrysemys picta marginata (Midland Pamted Turtle), Emydoidea blandingii (Blanding’s Turtle), 
and Clemmys guttata (Spotted Turtle). Two of these species are of particular interest; the Blanding’s Turtle and the Spotted 
Turtle have been designated as threatened by the Ohio Department of Natural Resources Division of Wildlife (2016). The first 
records for these tw'O species from Mentor Marsh include Clemmys guttata^ collected on 11 July 1931 by Roger Conant and 
Cecil Murphy (American Museum of Natural History reptile number 120799, formerly Toledo Zoological Society number 
541), and Emydoidea blandingii, collected on 1 1 July 1931 by Cecil Murphy (AMNH 120821, formerly TZS 542). Both of 
these specimens were collected on the “West end of Mentor Marsh.” It remains unclear whether the “West end of Mentor 
Marsh” refers to the eastern portion of the western basin (Figure 1 ) or to the western portion nearer the mouth of Mentor Harbor. 
While at the edge of Mentor Marsh (presumably on this date), Conant in 1982 related his observations of seemg numerous 
yellow spots at the water’s surface. Binoculars enabled them to identily the spots as yellow throats of Blanding’s Turtle. Conant 
WTote, “We had never seen so many in one place.” A second Emydoidea blandingii was collected on 16 June 1932 by Lawrence 
E. Hicks (Ohio State University Museum reptile number 877, formerly Hicks R420-1) at “Black Run Swamp.” Black Run 
Swamp probably refers to the southeastern portion of the marsh, wJiere Black Brook enters the marsh and becomes broadly 


16 



distributary, having no central channel (Isard 1966; Bernstein 1981; Whipple 1999). During the 1930s, the eastern part of the 
marsh was relatively open with cattails and nightshades, while buttonbush and alders formed dense stands of shrub growth. 
By 1951, the succession of swamp forest plant community had mostly replaced the open cattail-nightshade marsh community 
(Isard 1966; Whipple 1999). 

In 1959, intrusion of salt (sodium chloride) from the salt dump of salt mining tailings very near Black Brook in the southeastern 
comer of Mentor Marsh greatly elevated the salt concentration in the marsh and caused a die-off of native vegetation in the 
marsh and swamp forests (Isard 1966, 1967; NOACA 1983). Salt has persisted in the system and continues to pollute the marsh 
and has led to the establishment, proliferation, and vegetative dominance of Phragmites australis (common reed grass). This 
perturbation of the marsh in concert with human development and resultant fires have altered the marsh landscape (Bernstein 
1981; Fineran 2003; Isard 1967; Whipple 1999) to the point that it may no longer support Blanding’s and/or Spotted Turtles. 
Purposes of the project were to survey the turtles of Mentor Marsh and, more specifically, to search for the continued presence 
of Blanding’s and Spotted Turtles. 


Mentor Marsh 



Figure 1. Map of the Mentor Marsh area showing the basin outline and site locations. 


Methods 

Recent surveys and records of visual observations of the turtles of Mentor Marsh have been ongoing since 1979, when one 
of us (TOM) began vertebrate surveys of fishes, amphibians, reptiles, and mammals of the marsh. Turtle captures were also 
recorded marsh-wide during seining operations and during the deployment of turtle traps and fyke nets while conducting a 
fish survey for the Northeast Ohio Areawide Coordinating Agency (NOACA) in 1981 and 1982 (Matson 1983). A survey 
specifically for turtles was conducted during the summer of 2016 and was focused on the Mentor Harbor, Marsh Creek, 
and Becker Pond areas (Figure 1; sites 7-14) on the western end of the marsh and on the Shipman Pond area (sites 1-2) at 
the eastern end. Figure 1 diagrammatically represents where sites in the marsh were located; names of those sites and their 
respective geographical coordinates are presented in Table 1 . These two areas of the marsh were selected because they are 


17 





the areas approximating where earlier records of Emydoidea blaiidwgii and Clemmys guttata occurred and where suitable 
habitat may still occur. The section south of Shipman Pond (Figure 1, site 2) was trapped for small mammals during 1979; one 
Clemmys guttata was captured in a pitfall trap on 25 July 1979 and was released at the site of capture (Matson, unpublished 
data). All specimens collected, salvaged, or photo-vouchered were deposited in the herpetology and ichthyology collections of 
the Cleveland Museum of Natural History. 

Seines used in the surveys had lengths of 6 , 12, and 25 feet with 3/1 6-inch mesh, all had depths of 4 feet. Fyke nets had 3-foot 
hoops and two 25-foot wings with one-inch mesh. Turtle traps had hoop diameters of 2.5, 3, and 4 feet, all with one-inch square 
mesh. 

Scientific and common names used in this publication are those in Crother (2012). 


Table 1. Site locations in Mentor Marsh where turtle traps were positioned or observations of turtles were 
recorded over the period 1979-2016. Site 15 is approximate for 1932 Black Brook site. 


1 Site Number Site Name 

Latitude (N) 

Longitude (W) I 

1 

Shipman Pond 

41°45’08” 

81°17’31” 

2 

Shipman Pond SW 

4104437,, 

81017,47,, 

3 

Kervin North 

41°44’08” 

81°18’08” 

4 

Corduroy Road 

41°43;58” 

81°18’35” 

5 

SW Corduroy Road 

41°43’55” 

81°18’30” 

6 

Wake Robin Trail 

41043 , 45 ,, 

81°19’05” 

7 

Becker Pond 

41°43’34” 

81°19’48” 

8 

Marsh Creek Bridge 

41°43’28” 

81°20’18” 

9 

Canal zone 

41°43’27” 

81°20’16” 

10 

Dock E East 

41°43’2T’ 

81°20’23” 

11 

Dock D/1 

41°43’25” 

81°20’40” 

12 

Dock D/2 

41°43’27” 

81°20’47” 

13 

Dock D/Tip 

41043,31,, 

81°20’50” 

14 

Dock A 

41043 , 41 ,, 

81°20’53” 

15 

Blackbrook Mouth^ 

41044 , 

81°17’ 

16 

Spetz site 

41043,37,, 

81°20’16” 

17 

Near mouth of Mentor Harbor 

41°43’37” 

81°20’59.1” 

^available data do not pemit greater coordinate accuracy. 


Results 

During the 2016 trap survey, 74 trap-nights were accumulated (all turtle traps). From 1980-1982, 18 trap-nights using turtle 
hoop nets and lyke nets were deployed to capture both turtles and fish. Fyke nets were very effective in capturing turtles at 
some sites. For example, on 1 May 1982 tv^^o fyke nets placed at site 1, Shipman Pond, captured 12 Chelydra serpentina and 
71 Chrysemys picta marginata. 

Four species of turtles were trapped during 2016 (Table 2). Trachemys scripta elegans (Red-eared Slider) was first recorded for 
the marsh by James Spetz in May 2011 at a site in the western basin north of site 9 (CMNH 14202, James Spetz photo; Figure 
1, site 1 6). We trapped five adult individuals and observed one juvenile in Mentor Harbor of the western basin (Table 2; 1 turtle 
voLichered, CMNH 14543). This species was also sighted at site 6 on 12 October 2016 (CMNH 14544; Nanette Patrick photo) 
and in the eastern basin at site 1 on 22 June 2016 (Owen Locldiart, pers. comm.). 


18 



Sternotherus odoratus (Eastern Musk Turtle; 1 individual) was recorded for the first time from Mentor Marsh on 15 July 2016 
at site 10 (CMNH 14545); two additional musk turtles were trapped on 4 August, one each at sites 8 and 9. 

Chelydra serpentina and Chrysemys picta marginata were widely distributed throughout the marsh (Figure 1 and Table 2). 

The first documented record of Graptemys geographica (Eastern Map Turtle; 1 individual) in Mentor Marsh was captured in a 
fyke net at site 8 and released in August 1981 (Matson, unpublished data). On 1 July 2014, a specimen was trapped in Mentor 
Harbor (CMNH 14330; James Spetz photo). Map turtles were observed near the mouth of Mentor Harbor in 2015 near site 17 
(CMNH 14530; Jake Kudna photo). No map turtles were trapped or observed during our 2016 survey. 

There have been no additional records for Emydoidea blandingii since the 1930s or for Clemmys guttata since 1979. 


Table 2. Species of turtles recorded from Mentor Marsh, Take County, Ohio, and the sites at which they were detected, 
^indicates that the species is threatened within the state of Ohio (ODNR Division of Wildlife 2016). 


Species Name Site Numbers 

■ 

2 

3 

B 

5 

6 

7 

8 

9 

10 

1 1 

12 

13 

14 

15 

16 

17 

Family Chelydridae 

Chelydra serpentina 

Snapping Turtle 

• 



• 

• 

• 

• 

• 


• 

• 

• 

• 

• 




Family Kinosternidae 

Sternotherus odoratus 

Eastern Musk Turtle 








• 

• 

• 








Family Emydidae 

Chrysemys picta marginata 

Midland Painted Turtle 

• 

• 


• 

• 


• 

• 

• 

• 




• 




Clemmys guttata^ 

Spotted Turtle 


• 
















Emydoidea blandingiE 

Blanding’s Turtle 















• 


• 

Graptemys geographica 

Northern Map Turtle 








• 










Trachemys scripta elegans 

Red-eared Slider 

• 









• 

• 



• 


• 



Discussion 

Chrysemys picta marginata and Chelydra serpentina are widespread and common throughout the marsh. They have also 
colonized several mitigation ponds that were constructed in 2000 and 2001 above the marsh basin on the north and south sides 
of the marsh. Sternotherus odoratus was successfully trapped only in the western basin. Other areas within the marsh appear 
to provide suitable habitat to support this species and more extensive trapping may reveal its presence. The occurrences of 
Sternotherus within Mentor Marsh are the first records for this species in the Grand River drainage system. 

The occurrence of Trachemys scripta elegans in the western basin, along Wake Robin Trail in the central basin, and at Shipman 
Pond in the eastern basin was predictable. All three areas are frequented by people. The western basin marina is used extensively 
for recreation (sites 10-14), and the Marsh Creek and canal (sites 8-9) are used by canoeists and kayakers for outdoor education 
and recreation experiences. A boardwalk is available for public access at Wake Robin Trail (site 6), and Shipman Pond (site 1) 
is commonly used by fishermen and birdwatchers. These areas are closely proximate to roads whereby unwanted captive turtles 
could be released. Sliders have been released at numerous locales in northeastern Ohio; their populations and distribution are 
expanding, and it is probable that their numbers will increase in Mentor Marsh. These capture records are the first documented 
occurrences of Trachemys in the Grand River drainage system. 


19 


















The addition of new turtle species to the herpetofauna of Mentor Marsh was anticipated. Since the marsh is the old Grand River 
channel and floodplain, the species of turtles inhabiting the current Grand River are indicators of the species predictably present 
in the marsh. The Eastern Spiny Softshell Turtle {ApaJom spinifera) is common and widespread in the Grand River but has not 
yet been documented in Mentor Marsh. 

Management practices now used in Mentor Marsh in attempts to reduce the standing crop and distribution of Phragmites and to 
restore native plant biodiversity may lead to population increases in all turtle species. If still surviving in the marsh, the Spotted 
Turtle may be the species that would benefit most from habitat restoration. 


Acknowledgements 

We thanlcthe Kirtlandia Society, an associate society of the Cleveland Museum of Natural History, for supporting undergraduate 
student research assistants (Samantha Skerlec) and for many years in support of this and other projects. We also thank Lucy 
Weller for her continued financial support of research assistants (Dana Smith) through the Summer on the Cuyahoga Program. 


Literature Cited 

Bernstein, N.P. 1981. Vegetational history of Mentor Marsh. Ohio Journal of Science. 81(3): 105-1 08. 

Brockman, C.S. 2002. Physiographic regions of Ohio. Ohio Department of Natural Resources, Division of Geological Survey. 

2p, 

Conant, R. 1951. Reptiles of Ohio. The American Midland Naturalist. University of Notre Dame Press, Notre Dame, Indiana. 
284 p. 

Conant, R. 1982. Herpetology in Ohio: fifty years ago. Special Publication of the Toledo Herpetological Society. 64 p. 
Crother, B.I. (ed.). 2012. Standard common and current scientific names for North American amphibians, turtles, reptiles, and 
crocodilians. Seventh Edition. Herpetological Circular 39: 1-92. 

Fineran, S.A. 2003. Assessing spatial and temporal vegetative dynamics at Mentor Marsh, 1976-2000 A.D. Dissertation, The 
Ohio State University. 467 p. 

Holley, J.M. 1796. J. Milton Holley’s Diaiy: Cleaveland to Connecticut. Oct 1796, Western Reserve Historical Society. 
Cleveland, Ohio. 

Isard, L.G. 1966. The Vegetation of Mentor Marsh, A Preliminary Survey. The Cleveland Museum of Natural History, 
Cleveland, Ohio. 

Isard L.G. 1967. Biotic SuiTey of Mentor Marsh. The Cleveland Museum of Natural Histoiy, Cleveland, Ohio. 

Matson, T.O. 1983. An inventory of the species of fish occurring in Mentor Marsh. In Mentor Marsh, Lake County, Ohio 
Historical data and current baseline conditions. Final report, Technical appendix A49. Northeast Ohio Areawide 
Coordinating Agency. 

NOACA. 1983. Mentor Marsh, Lake County, Ohio Historical data and current baseline conditions. Final report. Technical 
appendix A49. Northeast Oliio Areawide Coordinating Agency. 

ODNRDW. 2016. Ohio’s listed species Wildlife that are considered to be endangered, threatened, species of concern, special 
interest, extirpated, or extinct in Ohio. Publication 5356. 

Pease, S. 1796. Seth Pease Field Notes: 1796. Western Reserve Historical Society. Cleveland, Ohio. 

Whipple, J.C. 1999. Geological and environmental assessment of Mentor Marsh. Master’s Thesis. University of Akron. Akron, 
Ohio. 

White, G.W. 1980. Glacial geology of Lake County, Ohio. Ohio Department of Natural Resources, Division of Geological 
Survey, Report of Investigations No. 1 1 7, Columbus, Ohio. 

Zemko, R.G. 1974. The occurrence and distribution of turtles in Ohio. M.S. thesis, Miami University, Oxford, OH. 98 p. 


20 



Ohio Biological Survey Notes 7: 21-33, 2017. © Ohio Biological Survey, Inc. 


A List of the Vascular Plants of Bender Mountain Preserve (Including Adjacent Parts of the 

Delhi Township Property and Sisters’ Hill) 

Denis Conover^*, Tim Sisson^, Dan Boone^, and Mary M. Riestenberg"^ 


'Dept. Biological Sciences, University of Cincinnati, Cincinnati, OH 45221-0006; ^Western Wildlife Corridor, P.O. Box 389077, Cincinnati, 
OH 45238; ^3228 Hanna Ave., Cincinnati, OH 45211; "'Dept of Biology, Mount St Joseph University, 5701 Delhi Ave., Cincinnati, OH 
45233. * Corresponding author; denis.conover@uc.edu 


Abstract: Several species of non-native invasive plants, including Amur honeysuckle {Lonicera maackii), had become 
quite numerous at Bender Mountain Preserve in Hamilton County, which made it very difficult for native plants to 
compete. After the removal of Amur honeysuckle by Western Wildlife Corridor volunteers, there was a resurgence 
of native plants in the preserve. So far, 431 species of vascular plants have been identified, 73% of which are native 
to Hamilton County. This list is sure to grow over the next few years as the preserve continues to recover. It is hoped 
that this study will encourage land managers and park districts not to give up on their nature preserves: non-native, 
invasive plants can be controlled in natural areas and native plants can come back. 

Key Words: Amur honeysuckle, native plants. Western Wildlife Corridor, Western Mesophytic Forest Region, Ohio 
River Valley 


Introduction 

Bender Mountain Nature Preserve (N 39. 10°, W 084.67°) is a 22.3 ha preserve in southwest Hamilton County, Ohio, consisting 
of property owned by Delhi Township Parks and Recreation as well as land owned by the Western Wildlife Corridor. The 
preserve and some of the adjacent forested property owned by the Sisters of Charity are managed by the Western Wildlife 
Corridor, a land trust dedicated to preserving the environmental heritage of the Ohio River Valley. Native plants reappeared 
at Bender Mountain Preserve after non-native invasive plants were removed by volunteers. This paper outlines the geologic 
history of Bender Mountain Preserve, its subsequent vegetational changes over time. Western Wildlife Corridor’s contribution 
to restoring the hillslope to its native state, and a list of plants that currently reside on the preserve. 

The Bender Mountain Preserve site lies at the southern edge of Delhi Township in Hamilton County, Ohio, on a steep ridge 
overlooking the Ohio River to the south and Rapid Run Creek to the north. The valleys of the Ohio River and its tributaries in 
this portion of Hamilton County are exceptionally narrow here and have oversteepened slopes due to the rerouting of the Ohio 
River during the Illinoian Glaciation. Approximately 400,000 years BP, during the Pleistocene Epoch, glaciation dammed the 
Pleistocene Deepstage Ohio River at Cincinnati (Durrell 1961, 1977). The large lake that formed as a result of the damming 
found an outlet at a location known as Anderson Ferry, west of downtown Cincinnati and about two kilometers southeast of 
present-day Bender Mountain. As glacial lake water overflowed the lake’s western terminus, it cut a new, narrow gorge in what 
is now the Ohio River valley. Tributary streams in the region where the river was rerouted also cut gorges as they dropped down 
to the level of the newly formed river. A small tributary of the Ohio River known as Rapid Run Creek flows in one of the newly 
formed gorges, and runs somewhat parallel to the Ohio River near Anderson Ferry. The ridge that formed between Rapid Run 
Creek and the Ohio River is Bender Mountain. 

Bender Mountain Preserve lies within the Outer Bluegrass Ecoregion (Hedeen 2006). The clay-rich soils on the preserve are 
categorized as members of the Eden Series by the Hamilton County Soil Survey (Eerch et al. 1980). The mountain’s ridge top 
is underlain by thin, stony silty-clay colluvial soil derived from the Ordovician Fairview Formation, whereas the lower part of 
the hillslope is underlain by thick clay colluvial soil derived from the underlying Kope Formation. Both formations consist of 
interbedded limestone and shale: the Fairview Formation is about 3:1 shale to limestone, and the Kope Formation is about 4:1 
shale to limestone. The dominance of shale in the Kope Formation allows it to weather into soil at a relatively fast rate, thus 
producing a thick, heavy clay soil that is associated with landsliding wherever the Kope Formation crops out in Cincinnati. A 
factor of safety analysis of saturated soils underlying the Bender hillslope indicates a residual friction angle of 16° to 20°. This 
suggests that the hillslope cannot retain soil at angles steeper than 20°, but the ridge slopes at a higher angle than this, especially 
near its western terminus. The soils on the hillside are most likely held in place by the rocky nature of the colluvial soil, along 


21 


with irregularities in the bedrock surface angles. Moreover, roots of woody plants contribute significant strength to the colluvial 
soil and allow it to remain in place, unfortunately intermittently, since the hillslope is pocked with landslide troughs and scarps 
(Riestenberg 1994). In fact, a road that cut tangentially across the hillslope had to be closed down permanently during the 1970s 
after a particularly dramatic series of landlsides (Fleming and Johnson 1994). 

The Bender Mountain area is a part of the Western Mesophytic Forest region, a region of diverse vegetation types (Braun 1950). 
The steep slopes, north and south aspects, and narrow valleys have created many different types of habitat, including dry, rocky 
ridge tops, warm, fertile, south-facing slopes, cool, fertile, north-facing slopes, alluvial benches, wetlands, and riparian zones. 

Delhi Township records indicate that over the years, parts of the Bender Mountain area have been used for grazing cows, 
foraging hogs, growing grapes and other fruit, and selective logging (Duba and Brunsman 1976). In the early part of the 
twentieth century, plant ecologist E. Lucy Braun mapped the woody plants on a hillslope north of the Ohio River at Anderson 
Ferry, close to present-day Bender Mountain (Braun 1916). Most of the same woody species can be found at Bender Mountain 
Preserve today; however, woody species are now under siege from invasion by alien plants and other pests such as the Emerald 
Ash Borer {Agrilus planipennis) (Jester 2009). 

Invasive alien plants began to appear in significant numbers in southwestern Ohio in the mid-twentieth century. For example, 
Braun noted in The Woody Plants of Ohio (Braun 1961) that Amur honeysuckle had by that time escaped from cultivation 
in Hamilton County and that it was becoming abundant in pastures and woodlands. By the year 2000, Amur honeysuckle 
covered most of Bender Mountain with a blanket of foliage that blocked the sun. Underneath this, other alien species such 
as garlic mustard {Alliaria petiolata) and winter creeper {Euonymus fortiinei), which are more shade tolerant, were gaining a 
foothold. The result was an observable reduction in the number of native plants, especially forest-floor, herbaceous flowering 
plants. When Western Wildlife Corridor began managing Bender Mountain Preserve in 2004, volunteers began removing the 
invasives, allowing the native plant species to repopulate the preserve (Conover et al. 2016; Conover and Sisson 2016). 


Methods 

Several books (listed in the Literature Cited section) were used to identify species. The Seventh Catalog of the Vascular Plants 
of Ohio (Cooperrider et al. 2001) provided the initial basis for the nomenclature used in this list of plants. Plant taxonomy is in 
a state of flux, and some of the names in this list have been updated to reflect recent changes in taxonomy. Author names are 
provided with each species to avoid confusion as to which species is present. For the most current taxonomic information about 
families, genera, and plant names, refer to The Integrated Taxonomic Information System (www.itis.gov). 

Most plants were identified in the field between 2013 and 2017. A few specimens were collected and deposited in herbaria at 
the University of Cincinnati and Miami University, Oxford, Ohio. 


Results 

Our vascular plant survey has so far identified 431 different species, of which 73% are native to Hamilton County. The list of 
species is sure to increase, since additional species are discovered in the preserve every year. The current list of species includes 
horsetails {Equisetum spp.), ferns, woody plants (shrubs, trees, and vines), rushes {Juncus spp.), sedges (Cyperus and Carex), 
grasses, and forbs. Plants such as blue-eyed Mary {Collinsia verna) grow in profusion on the gentle slope above Rapid Run 
creek; northern red oak (Quercus rubra), shagbark hickory {Carya ovata), great yellow wood sorrel {Oxalis grandis), early 
saxifrage {Saxifraga virginiensis), mullein-foxglove {Dasistoma macrophylla), American pennyroyal {Hedeoma pulegioides) 
and poverty oat grass (Danthonia spicata) prefer the upper slopes; and bulrushes (Scirpus spp.), jewel weeds {Impatiens spp.), 
scouring rushes {Equisetum spp.), and great blue lobelia {Lobelia siphilitica) prefer the wetter areas. From this study, it is clear 
that if Amur honeysuckle and other non-native invasive plants are removed from a natural area while propagules (seeds, roots, 
bulbs, and corms) of native plants are still viable, native vegetation can reclaim the area. 

The vascular plant species found in the Preserve are listed in Table 1 . 


Acknowledgements 

We wish to thank Rick Gardner, Don Geiger, John Homer, and Mike Vincent for help with the identification of certain plants. 


22 


Rick Gardner and Mike Vincent provided suggestions regarding the format of the species list. Riek Gardner also provided 
information regarding the native status of species on the list. Thanks are also due to Mike Vincent, curator of Miami University’s 
herbarium, and Eric Tepe, curator of the University of Cincinnati’s herbarium, for depositing specimens. Great appreciation is 
due to Western Wildlife Corridor for preserving Bender Mountain and for managing it properly. The removal of invasive plant 
speeies by Western Wildlife Corridor volunteers makes possible the continued survival of native plants and animals there. 


Table 1. List of vascular plants currently found on Bender Mountain. (*) indieates probably not native to Hamilton County. 


Acer saccharinum L. 

Silver maple 

Acer soccharum L. 

Sugar maple 

Family Amaranthaceae, the Amaranth Family 

*Achyranthes japonica 
(Miq.) Nakai 

Japanese chaff flower 

Family Anacardiaceae, the Cashew Family 

Rhus glabra L. 

Smooth sumac 

Rhus typhina L. 

Synonym: Rhus hirta (L.) 
Sudw. 

Staghorn sumac 

Toxicodendron ra dicans (L.) 
Kuntze 

Synonym: Rhus radicans L. 

Poison ivy 

Family Annonaceae, the Custard-Apple Family 

Asimina triloba (L.) Dunal. 

Paw paw 

Family Apiaceae, the Carrot Family (Umbelliferae) 

Chaerophyllum procumbens 
(L.) Crantz 

Spreading chervil 

*Conium macu latum L. 

Poison hemlock 

Cryptotoenia canadensis (L.) 
DC. 

Honewort 

*Daucus car Ota L. 

Wild carrot; Queen Anne's 
lace 

Erigenia bulbosa (Michx.) 
Nutt. 

Harbinger-of-spring 

Osmorhiza claytonii (Michx.) 
C. B. Blake 

Hairy sweet cicely 

Osmorhiza longistylis (Torn) 
DC. 

Smooth sweet cicely 

*Pastinaca sativa L. 

Wild parsnip 

Sanicula canadensis L. 

Canadian black snakeroot 

Sanicula odorata (Raf.) K. M. 
Pryer & L. R. Phillippe 

Clustered black snakeroot 

*Torilis sp. Ada ns. 

Hedge parsley 

Family Apocynaceae, The Dogbane Family 

Apocynum cannabinum L. 

Indian hemp 


PTERIDOPHYTES 

Family Aspleniaceae, the Spleenwort Family 

Asplenium platy neuron (L.) 
Britton, Sterns. & Poggenb. 

Ebony spleenwort 

Family Dryopteridaceae, the Wood Fern Family 

Cystopteris protrusa 
(Weath.) Blasdell 

Lowland fragile fern 

Diplazium pycnocarpon 
(Sprengel) M. Broun 

Synonym: Athyrium 
pycnocarpon (Sprengel) 
Tidestrom 

Narrow-leaved glade fern 

Polystichum acrostichoides 
(Michx.) Schott 

Christmas fern 

Family Equisetaceae, the Horsetail Family 

Eguisetum arvense L. 

Field horsetail 

Equisetum hyemale L. 

Scouring-rush 

GYMNOSPERMS 

Family Cupressaceae, the Cypress Family 

*Juniperus horizontalis 
Moench 

Creeping juniper 

Juniperus virginiana L. 

Eastern red cedar 

ANGIOSPERMS - Dicotyledons 

Family Acanthaceae, the Acanthus Family 

Rue Ilia strepens L. 

Smooth ruellia 

Family Adoxaceae, the Moschatel Family 

Sambucus canadensis L. 

Elderberry 

Viburnum prunifolium L. 

Blackhaw 

Family Aceraceae, the Maple Family 
(now included in the Sapindaceae) 

Acer negundo L. 

Boxelder 

Acer nigrum Michx. 

Synonym: Acer saccharum 

L. var. viride (Schmidt) E. 
Murray; Acer saccharum 

L. ssp. nigrum (f. Michx.) 
Desmarais 

Black maple 


23 
















* Vinca minor L. 

Periwinkle; myrtle 

Family Aquifoliaceae, the Holly Family 

Ilex opaca Aiton 

American holly 

Family Araliaceae, the Ginseng Family 

*Hedera helix L. 

English ivy 

Family Aristolochiaceae, the Birthwort Family 

Asarum canadense L. 

Wild ginger 

Family Asclepiadaceae, the Milkweed Family 
(now included in the Apocynaceae) 

Asclepias incarnata L. 

Swamp milkweed 

Asclepias syriaca L. 

Common milkweed 

Asclepias tuberosa L. 

Butterfly weed 

Cynanchum laeve (Michx.) 
Pers. 

Synonym: Ampelamus 
albidus (Nutt.) Britt.; 
Gonolobus laevis Michx. 

Sand vine 

Family Asteraceae, the Aster Family (Compositae) 

Achillea millefolium L. 

Yarrow 

Ageratina oltissimo (L.) R. 

M. King& H. Rob. 

White snakeroot 

Ambrosia artemisiifolia L. 

Common ragweed 

Ambrosia trifida L. 

Giant ragweed 

* Arctium minus Schk. 

Common burdock 

* Artemisia annua L. 

Annual wormwood 

* Artemisia vulgaris L. 

Mugwort 

Bide ns bipinnata L. 

Spanish needles 

Bide ns cernua L. 

Nodding bur-marigold 

Bidensfrondosa L. 

Devil's beggar-ticks 

*Carduus nutans L. 

Nodding thistle 

*Cichorum intybus L. 

Chicory 

*Cirsium arvense (L.) Scop. 

Canada thistle 

Cirsium discolor (Mu hi. ex 
Willd.) Sprengel 

Field thistle 

* Cirsium vulgare (Savi) Ten. 

Bull thistle 

Eclipta prostrata (L.) L. 
Synonym: Eclipta alba (L.) 
Hassk. 

Yerba-de-tajo 

Erechtites hierociifolio (L.) 

Raf. ex DC. 

Pilewort 

Erigeron annuus (L.) Pers. 

Daisy fleabane 


Erigeron canadensis L. 

Horseweed 

Erigeron philadelphicus L. 

Philadelphia fleabane 

Erigeron strigosus Muhl. ex 
Willd. 

White-top 

Eupatorium altissimum L. 

Tall boneset 

Eupatorium perfoliatum L. 

Boneset 

Eupatorium purpureum L. 

Purple joe-pye weed 

Eupatorium serotinum 

Michx. 

Late-flowering 

thoroughwort 

Euthamia graminifolia (L.) 
Nutt. 

Synonym: Solidago 
graminifolia (L.) Salisb. 

Bushy goldenrod 

Helianthus tuberosus L. 

Jerusalem artichoke 

Heliopsis helianthoides (L.) 
Sweet 

Ox-eye sunflower 

Lactuca canadensis L. 

Wild lettuce 

Lactuca floridana (L.) 
Gaertner 

Wild blue lettuce 

* Lactuca saligna L. 

Willow-leaf lettuce 

* Lactuca serriola L. var. 
serriola, var. integrota Gren. 

& Godr. 

Synonym: Lactuca scariola 
L. 

Prickly lettuce 

*Leucanthemum vulgare 

Lam. 

Ox-eye daisy 

*Pacl<era glabella (Poir.) C. 
Jeffrey 

Butterweed 

Polymnia canadensis L. 

Small-flowered leafcup 

Prenanthes alba L. 

White rattlesnake-root 

Rudbeckia laciniata L. 

Green-headed coneflower 

Rudbeckia triloba L. 

Brown-eyed Susan 

*Senecio vulgaris L. 

Common groundsel 

Silphium perfoliatum L. 

Indian cup 

Solidago altissima L. 

Tall goldenrod 

Solidago canadensis L. 

Canada goldenrod 

Solidago flexicaulis L. 

Zigzag goldenrod 

Solidago gigantea Aiton 

Smooth goldenrod 

Solidago nemo rails Aiton 

Gray goldenrod 

*Sonchus asper (L.) Hill 

Prickly sow-thistle 


24 









Symphyotrichum cordi folium 
(L.) Nesom 

Heart-leaved aster 

Symphyotrichum ericoides 
(L.) G.L. Nesom var. ericoides 

White heath aster 

Symphyotrichum 
lanceolatum (Willd.) Nesom 
ssp. lanceolatum var. 
lanceolatum 

Eastern lined aster 

Symphyotrichum 
lateriflorum (L.) A.& D. Love 
var. lateriflorum 

Calico aster 

Symphyotrichum novae- 
angliae (L.) Nesom 

New England aster 

Symphyotrichum shortii 
(Lindl.) Nesom 

Short's aster 

^Taraxacum officinale 

Weber ex F. H. Wigg. 

Common dandelion 

*Tussilagofarfara L. 

Colt's-foot 

Verbesina alternifolia (L.) 

Britt. 

Wingstem 

Synonym: Actinomeris 
alternifolia (L.) DC. 


Vernon ia gigontea (Walter) 
Trel. 

Tall ironweed 

Synonym: Vernonia 
altissima Nutt. 


Xanthium strumarium L. 

Common cocklebur 

Family Balsaminaceae, the Touch-me-not Family 

Impatiens capensis Meerb. 

Spotted jewelweed 

Impatiens pallida Nutt. 

Pale jewelweed 

Family Berberidaceae, the Barberry Family 

Caulophyllum thalictroides 
(L.) Michx. 

Blue cohosh 

Jeffersonia diphylla (L.) Pers. 

Twinleaf 

Podophyllum peltatum L. 

Mayapple 

Family Betulaceae, the Birch Family 

Carpinus carol iniana Walter 
ssp. virg iniana (Marshall) 
Furlow 

Musclewood; ironwood 

Ostrya virg iniana ( M i 1 1 e r) K . 
Koch 

Eastern hop-hornbeam 

Family Bignoniaceae, the Trumpet-creeper Family 

Campsis radicans (L.) 
Seemann 

Trumpet-creeper 


Family Boraginaceae, the Borage Family 


Hackelia virg iniana (L.) 1. M. 
Johnston 

Beggar's-lice 

Mertensia virginica (L.) Pers. 
ex Link 

Virginia bluebells 

Family Brassicaceae, the Mustard Family (Cruciferae) 

*Alliaria petiolata (Bieb.) 
Cavara & Grande 

Synonym: Alliaria 
officinalis Andrz. 

Garlic mustard 

*Barbarea verna (Mill.) 

Asch. 

Early yellowrocket 

* Bar bare a vulgaris R. Br. 

Winter cress 

Boechera laevigata (Muhl. 
ex Willd.) Al-Shehbaz 

Smooth rockcress 

* Brass! ca nigra L. 

Black mustard 

*Capsella bursa-pastoris (L.) 
Medikus 

Shepherd's purse 

Cardamine concatenata 
(Michx.) 0. Schwarz 

Synonym: Dentaria 
laciniata Muhl. 

Cut-leaved toothwort 

Cardamine diphylla (Michx.) 
A. Wood 

Synonym: Dentaria 
diphylla Michx. 

Twin-leaved toothwort 

Cardamine douglasii Britton 

Purple cress 

*Cardamine hirsuta L. 

Hoary bitter cress 

*Erophila verna (L.) Chev. 

Whitlow-grass 

*Hesperis matronal is L. 

Dame's rocket 

lodanthus pinnatifidus 
(Michx.) Steudel 

Purple rocket 

*Lepidium cam pest re (L.) 

R. Br. 

Field pepper-weed 

Lepidium virginicum L. 

Poor-man's pepper 

Rorippa palustris (L.) Besser. 

Common yellow-cress 

*Thlaspi arvense L. 

Field penny-cress 

Family Caesalpiniaceae, the Caesalpinia Family 
(now in Fabaceae) 

Cercis canadensis L. 

Redbud 

Gleditsia triacanthos L. 

Honey-locust 

Gymnocladus dioica (L.) K. 
Koch. 

Kentucky coffee-tree 


25 











Family Campanulaceae, the Bellflower Family 


Family Convolvulaceae, the Morning-Glory Family 


Campanula americana L. 
Synonym: 

Campanulastrum 
americanum (L.) Small 

Tall bellflower 

Lobelia inflata L. 

Indian tobacco 

Lobelia siphilitica L. 

Great blue lobelia 

Triodanis perfoliata (L.) 
Nieuwl. 

Venus' looking-glass 

Family Cannabaceae, the Hemp Family 

Celtis occidentolis L. 

Hackberry 

Family Caprifoliaceae, the Honeysuckle Family 

*Lonicera japonica Thunb. 

Japanese honeysuckle 

*Lonicera maackii (Rupr.) 
Maxim. 

Amur honeysuckle 

Symphoricarpos orbiculotus 
Moench. 

Coral berry 

Family Caryophyllaceae, the Pink Family 

Paronychia canadensis (L.) 
Alph. Wood 

Forked chickweed 

*Saponaria officinalis L. 

Soapwort; Bouncing Bet 

Stellaria corei Shinners 

Kentucky chickweed 

*Stellorio medio (L.) Vill. 

Common chickweed 

* Stellaria pallida (Dumort) 

Pi re 

Lesser chickweed 

Stellaria pubera Michx. 

Star chickweed 

Family Celastraceae, the Staff-Tree Family 

*Celastrus orbiculotus 

Thunb. 

Oriental bittersweet 

*Euonymus alatus (Thunb.) 
Siebold 

Winged Euonymus 

Euonymus atropurpureus 
Jacq. 

Wahoo 

* Euonymus fortune! (Turcz.) 
Hand.-Mazz. 

Wintercreeper 

Family Chenopodiacaeae, the Goosefoot Family 
(now included in the Amaranthaceae) 

*Chenopodium album L. 

Lamb's quarters 

Dysphania ombrosioides (L.) 
Mosyakin & Clemants 

Mexican tea 

Chenopodium stondleyonum 
Aellen 

Woodland goosefoot 


Colystegio sepium (L.) R. Br. 
Synonym: Convolvulus 
sepium L. 

Hedge bindweed 

*lpomoea hederocea Jacq. 

Ivy-leaved morning-glory 

Ipomoea lacunosa L. 

Small-flowered morning- 
glory 

Ipomoea pandurata (L.) G. F. 
W. Mey 

Man-of-the-earth 

Family Cornaceae, the Dogwood Family 

Cornus drummondii C. A. 
Meyer 

Rough-leaved dogwood 

Cornus florida L. 

Flowering dogwood 

Cornus racemosa Lam. 

Gray dogwood 

Family Cuscutaceae, the Dodder Family 

Cuscuta pentogona Engelm. 

Five-angled dodder 

Family Crassulaceae, the Stonecrop Family 

Sedum ternatum Michx. 

Wild stonecrop 

Family Dipsacaceae, the Teasel Family 
(now included in the Caprifoliaceae) 

*Dipsacusfullonum L. 
Synonym: Dipsacus 
sylvestris Huds. 

Common teasel 

* Dipsacus loci n lotus L. 

Cut-leaved teasel 

* Dipsacus sativus (L.) 

Honck. 

Indian teasel 

Family Ebenaceae, the Ebony Family 

Diospyros virginiana L. 

Persimmon 

Family Euphorbiaceae, the Spurge Family 

Acalypha deamii (Weath.) 
H.E. Ahles 

Deam's three-seeded 

mercury 

Acalypha rhomboidea Raf. 
Synonym: Acalypha 
virginica L. var. 
rhomboidea (Raf.) 

Cooperr. 

Rhombic three-seeded 

mercury 

Acalypha virginica L. 

Virginia three-seeded 
mercury 

Euphorbia commutata 
Engelm. ex A. Gray 

Woodland spurge 

Family Fabaceae, the Pea 
(Leguminosae) 

or Bean Family 

*Albizia julibrissin Durazz. 

Silk tree 


26 


















Family Hydrangeaceae, the Hydrangea Family 


Amphicarpaea bracteata (L.) 
Fernald 

Hog-peanut 

Desmonthus illinoensis 
(Michx.) MacMillan 

Prairie mimosa 

* Lotus corniculata L. 

Birdsfoot trefoil 

*Medicago lupulina L. 

Black medick 

*Melilotus albus Medik. 

White sweet-clover 

*Melilotus officinalis (L.) 

Pall. 

Yellow sweet-clover 

Robinio pseudoacacia L. 

Black locust 

* Securigera varia (L.) 

Lassen 

Crown-vetch 

*Trifolium hybridum L. 

Alsike clover 

* Trifolium prate nse L. 

Red clover 

*Trifolium re pens L. 

White clover 

Family Fagaceae, the Beech Family 

Fag us grandifolia Ehrh. 

American beech 

Quercus alba L. 

White oak 

Quercus macrocar pa Michx. 

Bur oak 

Quercus muhlenbergii 

Engelm. 

Chinquapin oak 

Quercus rubra L. 

Synonym: Quercus 
borealis F. Michx. 

Northern red oak 

Quercus shumardii Buckley 

Shumard oak 

Quercus velutina Lam. 

Black oak 

Family Fumariaceae, the Fumitory Family 
(now included in the Papaveraceae) 

CorydalisfJavula (Raf.) DC. 

Yellow corydalis 

Dicentra canadensis (Goldie) 
Walp. 

Squirrel corn 

Dicentra cucullaria (L.) 

Bernh. 

Dutchman's-breeches 

Family Geraniaceae, the Geranium Family 

Geranium carolinianum L. 

Carolina crane's-bill 

Geranium maculatum L. 

Wild geranium 

Family Hippocastanaceae, the Horse-Chestnut Family 
(now included in the Sapindaceae) 

Aesculus glabra Willd. 

Ohio buckeye 

Aesculus flava Alton 

Synonym: Aesculus 
octandra Marshall. 

Yellow buckeye 


Hydrangea arborescens L. 

Wild hydrangea 

*Philadelphus coronarius L. 

Mock-orange 

Family Hydrophyllaceae, the Waterleaf Family 
(now included in the Boraginaceae) 

Hydrophyllum 
appendiculatum Michx. 

Appendaged waterleaf 

Hydrophyllum canadense L. 

Maple-leaved waterleaf 

Hydrophyllum 
macrophyllum Nutt. 

Large-leaved waterleaf 

Phacelia bipinnatifida 

Michx. 

Fernleaf phacelia 

Family Hypericaceae, the St. John’s-Wort Family 

*Hypericum perforatum L. 

Common St. John's-wort 

Hypericum punctatum Lam. 

Spotted St. John's-wort 

Family Juglandaceae, the Walnut Family 

Cary a cordiformis 
(Wangenh.) K. Koch 

Bitternut hickory 

Cary a laciniosa (Michx. f.) 
Loudon 

Shellbark hickory 

Carya ovata (Miller) K. Koch 

Shagbark hickory 

Juglans nigra L. 

Black walnut 

Family Lamiaceae, the Mint Family (Labiatae) 

Agastache nepetoides (L.) 
Ktze. 

Yellow giant-hyssop 

Blephilia hirsuta (Pursh) 

Benth. 

Hairy woodmint 

*Glechoma hederacea L. 

Ground ivy; gill-over-the- 
ground; creeping Charlie 

Hedeoma pulegioides (L.) 

Pers. 

American pennyroyal 

*Lamium amplexicaule L. 

Henbit 

*Lamium purpureum L. 

Purple dead-nettle 

*Leonurus cardiaca L. 

Motherwort 

Lycopus virginicus L. 

Virginia water-horehound 

Prunella vulgaris L. 

Self-heal; heal-all 

Salvia lyrata L. 

Lyre-leaved sage 

Scutellaria ovata Hill 

Heart-leaved skullcap 

Stachys nuttallii Benth. 
Synonym: Stachys riddellii 
House.; Stachys cordata 
Riddell. 

Heart-leaved hedge-nettle 

Stachys tenuifolia Willd. 

Common hedge-nettle 


27 













Teucrium canadense L. 

American germander; 
wood sage 

Family Lauraceae, the Laurel Family 

Lindera benzoin (L.) Blume 

Northern spicebush 

Sassafras a Ibid urn (Nutt.) 
Nees. 

Sassafras 

Family Limnanthaceae, the Meadow-Foam Family 

Floerkea proserpinacoides 
Willd. 

False mermaid 

Family Lythraceae, the Loosestrife Family 

*Lythrum salicaria L. 

Purple loosestrife 

Family Magnoliaceae, the Magnolia Family 

Liriodendron tulipifera L. 

Tuliptree; yellow poplar 

Family Malvaceae, the Mallow Family 

*Abutilon theophrasti 

Medic. 

Velvet-leaf 

Hibiscus moscheutos L. 

Crimsoneyed rosemallow 

*Hibiscus syriacus L. 

Rose of Sharon 

*Sida spinoso L. 

Prickly mallow 

Family Menispermaceae, the Moonseed Family 

Menispermum canadense L. 

Moonseed 

Family Molluginaceae, the Carpet- Weed Family 

* Mol logo verticil lata L. 

Carpet-weed 

Family Montiaceae, the Links Family 

Claytonia virginico L. 

Spring beauty 

Family Moraceae, the Mulberry Family 

*Morus alba L. 

White mulberry 

Morus rubra L. 

Red mulberry 

Family Oleaceae, the Olive 

Family 

Fraxinus americana L. 

White ash 

Fraxinus quadrangulata 
Michx. 

Blue ash 

*Ligustrum vulgare L. 

Common privet 

Family Onagraceae, the Evening-Primrose Family 

Circaea lutetiana L. var. 
canadensis L. 

Enchanter's nightshade 

Epilobium coloratum Biehler 

Purple-leaved willow-herb 

Gaura biennis L. 

Biennial gaura 

Oenothera biennis L. 

Common evening-primrose 


Family Orobanchaceae, the Broomrape Family 

Dasistoma nnacrophylla 
(Nutt.) Raf. 

Synonym: Sey maria 
macrophylla Nutt. 

Mullein-foxglove 

Family Oxalidaceae, the Wood Sorrel Family 

Oxalis dillenii Jacq. 

Southern yellow wood- 
sorrel 

Oxalis grandis Small 

Great yellow wood-sorrel 

Oxalis purpurea L. 

Purple wood-sorrel 

Oxalis stricto L. 

Synonym: Oxalis europaea 
Jord. 

Common yellow wood- 
sorrel 

Family Papaveraceae, the Poppy Family 

Sanguinaria canadensis L. 

Bloodroot 

Stylophorum diphyllum 
(Michx.) Nutt. 

Synonym: Chelidonium 
diphyllum Michx. 

Wood poppy; celandine 
poppy 

Family Passifloraceae, the Passion-Vine Family 

Passiflora luteo L. 

Yellow passion-flower 

Family Penthoraceae, the Ditch-Stonecrop Family 

Penthorum sedoides L. 

Ditch-Stonecrop 

Family Phrymaceae, the Lopseed Family 

Phryma leptostochyo L. 

American lopseed 

Family Phytolaccaceae, the Pokeweed Family 

Phytolacca americana L. 

Pokeweed 

Family Plantaginaceae, the Plantain Family 

Collinsia verna N utt. 

Blue-eyed Mary 

Leucosporo multifida 
(Michx.) Nutt. 

Synonym: Conobea 
multifida (Michx.) Benth. 

Narrowleaf paleseed 

*Plantago lanceolata L. 

English plantain 

*Plantago major L. 

Broad-leaved plantain 

Plantago rugelii Decne. 

Rugel's plantain 

Veronica anagallis-aquatica 

L. 

Water speedwell 

Veronica peregrina L. 

Purslane speedwell 

Family Platanaceae, the Plane-Tree Family 

Platanus occidentalis L. 

American sycamore 


28 
























Family Polemoniaceae, the Phlox Family 


Phlox divaricata L. 

Blue phlox 

Polemonium reptans L. 

Greek valerian 

Family Polygonaceae, the Smartweed Family 

*Fallopia japonica (Houtt.) 
Ronse Deer. 

Japanese knotweed 

Persicaria hydropiper (L.) 
Spach 

Water-pepper 

* Persicaria longiseta (Bruijn) 
Kitag. 

Long-bristled smartweed 

* Persicaria maculosa Gray 

Lady's thumb 

Persicaria punctata (Elliott) 
Small 

Dotted smartweed 

Persicaria virginiana (L.) 
Gaertn. 

Jumpseed; Virginia 
knotweed 

*Polygonum aviculare L. 

Prostrate knotweed 

*Rumex crisp us L. 

Curly dock 

*Rumex obtusifolius L. 

Bitter dock 

Family Portulacaceae, the Purslane Family 

Claytonia virginica L. 

Spring beauty 

Portulaca oleracea L. 

Common purslane 

Note: There is 
archeological evidence 
indicating that this 
species is native. 

Family Primulaceae, the Primrose Family 

*Anagallis arvensis L. 

Scarlet pimpernel 

*Lysimachia nummularia L. 

Moneywort 

Samolus parviflorus Raf. 
Synonym: Samolus 
floribundus Kunth 

Water-pimpernel 

Family Ranunculaceae, the Buttercup Family 

Anemone acutiloba (DC.) G. 
Lawson 

Synonym; Hepotico 
acutiloba DC.; Hepatica 
nobilis Schreb. var. acuta 
(Pursh) Steyerm. 

Sharp-lobed hepatica 

Anemone virginiana L. 

Thimbleweed 

Cimicifuga racemosa (L.) 

Nutt. 

Synonym: Actaea 
racemosa L. 

Black cohosh 

Delphinium tricorne Michx. 

Dwarf larkspur 


Isopyrum biternatum (Raf.) 
Torn & A. Gray 

Synonym: Enemion 
biternatum Raf. 

False rue-anemone 

Ranunculus abortivus L. 

Kidney-leaved crowfoot 

*Ficaria verna Huds. 

Lesser celandine 

Ranunculus hispidus 

Michx. var. hispidus; var. 
caricetorum (Greene) T. 
Duncan 

Synonym: Ranunculus 
septentrionalis Poiret 

Hispid buttercup 

Ranunculus micranthus 

Nutt. 

Small-flowered crowfoot 

Ranunculus recurvatus 

Poiret 

Hooked crowfoot 

Thalictrum dioicum L. 

Early meadow-rue 

Thalictrum thalictroides (L.) 
A. J. Fames & B. Bovin 

Rue-anemone 

Family Rosaceae, the Rose Family 

Crataegus mollis Scheele 

Downy hawthorn 

*Duchesnea indica 
(Andrews) Teschem. 

Indian strawberry 

Geum canadense Jacq. 

White avens 

Geum vernum (Raf.) Torn & 

A. Gray 

Spring avens 

* Mai us pumila Mill. 
Synonym: Pyrus malus L. 

Cultivated apple 

Prunus americana Marshall 

Wild plum 

*Prunus avium L. 

Sweet cherry 

Prunus serotina Ehrh. 

Wild black cherry 

*Pyrus calleryana Dene. 

Callery pear 

*Rosa canina L. 

Dog rose 

*Rosa multi flora Thunb. Ex 
Murray 

Multiflora rose 

Rosa setigera Michx. 

Prairie rose; climbing rose 

Rubus allegheniensis T. C. 
Porter 

Common blackberry 

Rubus ensleniiJratt. 

Enslen's blackberry 

Rubus flagellaris Willd. 

Northern dewberry 

Rubus occidentalis L. 

Black raspberry 

Family Rubiaceae, the Madder Family 

Galium aparine L. 

Cleavers 

Galium circaezans Michx. 

Wild licorice 


29 











Galium concinnum Torn & 

A. Gray 

Shining bedstraw 

*Galium mollugo L. 

False baby's breath 

Family Rutaceae, the Rue Family 

Ptelea trifoliata L. 

Wafer-ash 

Family Salicaceae, the Willow Family 

Populus delta ides Marshall 

Cottonwood 

Salixexigua Nutt. ssp. 
interior (Rowlee) Cronq. 
Synonym: Salix interior 
Rowlee. 

Sandbar willow 

Salix nigra Marshall 

Black willow 

Family Saxifragaceae, the Saxifrage Family 

Heuchera americana L. 

Alum-root 

Saxifraga virginiensis Michx. 

Early saxifrage 

Family Scrophulariaceae, the Figwort Family 

Scrophularia marilandica L. 

Maryland figwort 

* Verbascum blatteria L. 

Moth mullein 

* Verbascum thapsus L. 

Common mullein 

Family Simaroubaceae, the Quassia Family 

*Ailanthus altissima (Miller) 
Swingle 

Tree-of-heaven 

Family Solanaceae, the Nightshade Family 

Physalis longifolia Nutt. var. 
subglabrata (Mackenz. & 
Bush) Cronq. 

Smooth groundcherry 

Solanum carolinense L. 

Horse-nettle 

Solanum dulcamara L. 

Bittersweet nightshade 

*Solanum lycopersicum L. 

Garden tomato 

Solanum ptychanthum DC. 

Black nightshade 

Family Staphyleaceae, the Bladder-Nut Family 

Staphylea trifolia L. 

Bladdernut 

Family Tiliaceae, the Linden Family 

7/7/0 heterophylla Vent. 

White basswood 

Tilia americana L. 

American linden 

Family Ulmaceae, the Elm Family 

Ulmus americana L. 

American elm 

Ulmus rubra Mu hi. 

Slippery elm; red elm 

Family Urticaceae, the Nettle Family 

Laportea canadensis (L.) 
Wedd. 

Wood nettle 


Pi lea pumila (L.) A. Gray 

Clearweed 

Urtica dioica L. var. procera 
(Muhl. ex Willd.) Wedd. 
Synonym: Urtica dioica 

L. subsp. gracilis (Alton) 
Selander 

American stinging nettle 

Family Verbenaceae, the Vervain Family 

Phyla lanceolata (Michx.) 
Greene 

Synonym: Lippia lanceolata 
Michx. 

Fog-fruit 

Verbena utricifolia L. 

White vervain 

Family Violaceae, the Violet Family 

Viola pubescens Ait. 

Common yellow violet 

Viola sororia Willd 

Synonym: Viola 
papilonacea Pursh 

Common blue violet 

Viola striata Alton. 

Striped violet 

Family Vitaceae, the Grape Family 

Parthenocissus quinquefolia 
(L.) Planchon 

Virginia creeper 

Vitis vulpina L. 

Frost grape 

ANGIOSPERMS - Monocotyledons 

Family Asparagaceae, the Asparagus Family 

*Yucca filamentosa L. 

Adam's needle; yucca 

Family Araceae, the Arum Family 

Arisaema dracontium (L.) 
Schott 

Green dragon 

Arisaema triphyllum (L.) 
Schott 

Synonym: Arisaema 
atrorubens (Alton) Blume 

Jack-in-the-pulpit 

Family Commelinaceae, the Spiderwort Family 

*Commelina communis L. 

Asiatic day-flower 

Trodescantia subaspera Ker 
Gawl. 

Zigzag spiderwort 

Tradescantia virginiana L. 

Virginia spiderwort 

Family Cyperaceae, the Sedge Family 

Carex aggregata Mackenzie 
Synonym: Carex 
sparganioides var. 
aggregata (Mack.) 

Gleason 

Glomerate sedge 


30 





















Juncus spp. 

Rushes 

J uncus tenuis Willd. 

Path rush 

Juncus torreyi Coville 

Torrey's rush 

Family Liliaceae, the Lily Family 

Allium burdickii (Hanes) A. 

G. Jones 

Synonym: Allium 
tricoccum Aiton var. 
burdickii Hanes 

Narrow-leaved ramp 

Allium conadense L. 

Wild garlic 

Allium cernuum Roth 

Nodding wild onion 

Allium tricoccum Aiton 

Red ramp 

* Allium vineale L. 

Field garlic 

Camassia sell bides (Raf.) 
Cory 

Synonym: Cyanotris 
scilloides Raf. 

Wild hyacinth 

Erythronium albidum Nutt. 

White trout-lily 

Erythronium americanum 

Ker Gawler 

Yellow trout-lily 

*Hemerocallisfulva (L.) L. 

Day-lily 

Maianthemum racemosum 
(L.) Link 

Synonym: Smilacina 
racemosa (L.) Desf. 

Solomon's plume; false 
Solomon's seal 

*Ornithogalum umbellatum 
L. 

Star-of-Bethlehem 

Polygonatum biflorum 
(Walter) Elliott 

Solomon's seal 

Polygonatum commutatum 
(Schult. & Schult. f.) A. Dietr 
Synonym: Polygonatum 
biflorum (Walter) Elliott 
var. commutatum (Schult. 
f.) Morong 

Giant Solomon's seal 

Trillium flexipes Raf 

Synonym: Trillium 
gleasonii Fern. 

Drooping trillium 

Trillium sessile L. 

Sessile trillium 

Uvularia grandiflora 
(Michx.) Salisb. 

Large-flowered bellwort 

Family Poaceae, the Grass 

Family (Graminae) 

*Agrostis gigantea Roth 
Synonym: Agrostis 
stolonifera L. var. major 
(Gaudin) Farw.; Agrostis 
alba L, misapplied. 

Redtop 


Carex albicans Willd. 
Synonym: Carex artitecta 
Mackenzie 

Oak sedge 

Carex albursina Sheldon 

White bear sedge 

Carex blanda Dewey 

Common wood sedge 

Carex brevior {Dewey) Mack. 

Shortbeak sedge 

Carex careyana Torn ex 
Dewey 

Carey's sedge 

Carex cephalophora Muhl. 
ex Willd. 

Oval-leaf sedge 

Carex communis L.H. Bailey 

Fibrousroot sedge 

Carex frankii Kunth 

Frank's sedge 

Carex granu laris Muhl. ex 
Willd. 

Limestone meadow sedge 

Carex g rise a Wahlenb. 

Inflated narrow-leaf sedge 

Carex jamesii Schwein. 

James' sedge 

Carex pensylvanica Lam. var. 
pensylvanica 

Pennsylvania sedge 

Carex rosea Schkuhr ex 

Willd. 

Rosy sedge 

Carex sparganioides Muhl. 
ex Willd. 

Bur-reed sedge 

Carex spp. 

Sedges 

Carex tribuloides Wahlenb. 

Blunt broom sedge 

Carex vulpinoidea Michx. 

Fox sedge 

Cyperus esculentes L. 

Yellow nut-grass 

Cyperus strigosus L. 

Straw-colored flatsedge 

Scirpus atrovirens Willd. 

Dark green bulrush 

Scirpus pend ulus Muhl. 
Synonym: Scirpus lineatus 
Michx. 

Drooping bulrush 

Family Dioscoreaceae, the Yam Family 

Dioscorea villosa L. 

Wild yam 

Family Iridaceae, the Iris Family 

Sisyrinchium angustifolium 
Miller 

Common blue-eyed-grass 

Family Juncaceae, the Rush Family 

Juncus dudleyi Wiegand 
Synonym: Juncus tenuis 
Willd. var. dudleyi 
(Wiegand) F. J. Hermann 

Dudley's rush 

Juncus effusus L. var. solutus 
Fern. & Wieg. 

Common rush 


31 









Alopecurus carolinianus 
Walter 

Meadow foxtail 

Andropogon virginicus L. 

Broomsedge 

*Bromus inermis Leyss. 

Smooth brome 

*Bromus japonicus Thunb. 
ex Murray 

Japanese brome 

*Dactylis glome rata L. 

Orchard grass 

Danthonia spicata (L.) P. 
Beauv. ex Roem. & Schult. 

Poverty oat grass 

*Digitaria ischaemum 
(Schreb.) Muhl. 

Smooth crab-grass 

*Digitaria sangui nails (L.) 
Scop. 

Large crab-grass 

*Echinochloa crusgalli (L.) P. 
Beauv. var. crusgalli 

Barnyard grass 

Echinochloa muricata (P. 
Beauv.) Fern. 

Barnyard grass 

Elymus hystrix L. 

Synonym: Hystrix patula 
Moench 

Bottlebrush-grass 

Elymus macgregorii R. 

Brooks & J.J.N. Campbell 

Early wild rye 

*Elymus repens (L.) Gould 

Quackgrass 

Elymus riparius Wieg. 

Streambank wild rye 

Elymus villosus Muhl. ex 
Willd. 

Downy wild rye 

Elymus virginicus L. var. 
virginicus 

Virginia wild rye 

*Festuca arundinacea 

Schreb. 

Tall fescue 

*Festuca pratensis Hudson 

Meadow fescue 

Festuca subverticillata (Pers) 
E. Alexeev 

Synonym: Festuca obtusa 
Biehler 

Nodding fescue 

Glyceria striata (Lam.) A. 
Hitchc. 

Fowl manna grass 

Hordeum pusillum Nutt. 

Little barley 


Leersia virginica Willd. 

White grass 

*Microstegium vimineum 
(Trin.) A. Camus. 

Japanese sblt grass 

Muhlenbergia schreberi ]. F. 
Gmelin. 

Nimblewill 

Panicum dichotomiflorum 
Michx. 

Fall panic grass 

Panicum spp. 

Panic grasses 

*P ha laris arundanacea L. 

Reed canary grass 

*Phleum pratense L. 

Timothy 

*Phragmites australis (Cav.) 
Trin. ex Steud. 

Common reed 

*Poa annua L. 

Annual blue grass 

*Poa pratensis L. 

Kentucky blue grass 

Poa sylvestris Gray 

Woodland blue grass 

*Setaria faberi Herrm. 

Giant foxtail grass 

*Setaria glauca (L.) Beauv. 

Yellow foxtail grass 

*Setaria viridis (L.) Beauv. 

Green foxtail grass 

* Sorghum halepense (L.) 

Pers. 

Johnson grass 

Sphenopholis nitida (Biehler) 
Scribn. 

Shiny wedgescale 

Sporobolus spp. 

Sporobolus 

Sporobolus vaginifiorus 
(Torn ex A. Gray) A. Wood 

Poverty-grass 

Tridens fiovus (L.) A. Hitchc. 
Synonym: Triodia flava (L.) 
Smyth 

Grease grass 

Family Smilaceae, the Catbrier Family 

Smilax herbacea L. 

Carrion-flower 

Smilax tamnoides L. 

Synonym: Smilax hispida 
Muhl. ex Torn; Smilax 
tamnoides L. van hispida 
(Muhl. ex Torn) Fern. 

Bristly greenbrier 

Family Typhaceae, the Cattail Family 

Typha angustifolia L. 

Narrowleaf cattail 


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Braun, E.L. 1961. The woody plants of Ohio. Ohio State University Press, Columbus, Ohio. 362 p. 


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