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Effect  of  Gate  Installation 

on  Continued  Use  by  Bats 

of  Four  Abandoned  Mine 

Workings  in 

Western  Montana 


A  Report  to: 

Montana  Department  of  Environmental  Quality 
Mine  Waste  Cleanup  Bureau 

2209  Phoenix  Avenue 
Helena,  Montana  59620-0901 


Submitted  by: 
Paul  Hendricks 


December,  1999 


MONTANA 


Natural  Heritage 
Program 


599.41518 
N11EGI 
-  1999 
1 


^»fLb(Lc.l 


Montana  State  Library 


3  0864  1004  6971   0 


ox  aanssi 


EFFECT  OF  GATE  INSTALLATION 

ON  CONTINUED  USE  BY  BATS 

OF  FOUR  ABANDONED  MINE  WORKINGS 

IN  WESTERN  MONTANA 


December  1999 


°  1999  Montana  Natural  Heritage  Program 


State  Library  Building,  P.O.  Box  201800,  1515  East  Sixth  Avenue.  Helena,  MT  59620-1800.  406-444-3009 


This  document  should  be  cited  as  follows: 

Hendricks,  P.   1999.  Effect  of  gate  installation  on  continued  use  by  bats  of  tour  abandoned  mine  workings  in  western 
Montana.  Unpublished  report  to  Montana  Department  of  Environmental  Quality.  Montana  Natural  Heritage  Program. 
Helena.   13  pp. 


ACKNOWLEDGMENTS 

This  project  was  funded  by  the  Montana  Department  of  Environmental  Quality,  Mine 
Waste  Cleanup  Bureau,  under  DEQ  Contract  No.  480008  to  the  Montana  Natural  Heritage 
Program,  Natural  Resources  Information  System,  Montana  State  Library.  Special  thanks  to  Jack 
Yates  (DEQ)  for  his  continued  support  of  this  work,  to  Lee  Flath  (Lewis  and  Clark  Caverns  State 
Park)  for  his  cooperation  and  interest  in  the  project,  and  to  Marian  and  Max  Johnson  of  Ravalli 
for  permission  to  access  the  McDonald  Mine.  Tom  O'Shea  (USGS-Biological  Resources 
Division)  kindly  loaned  the  data  loggers  used  during  this  project.  Sam  Martinez  helped  with  the 
surveys  and  recorded  climate  data  during  them. 


INTRODUCTION 

In  1996  the  Mine  Waste  Cleanup  Bureau  of  the  Montana  Department  of  Environmental 
Quality  installed  culvert  gate  systems  in  the  portals  of  four  abandoned  mine  adits  in  western 
Montana    Two  gates  were  installed  at  the  McDonald  ("Ravalli")  Mine  adits  in  Lake  County,  and 
two  more  were  placed  in  portals  at  the  Gypsum  Mine  workings  of  Lewis  and  Clark  Caverns  State 
Park  in  Jefferson  County    Inspection  of  these  mine  adits  prior  to  gate  installation  revealed  that 
each  was  used  at  some  time  during  the  year  by  bats,  particularly  Townsend's  Big-eared  Bat 
(Connor hi  mis  townsendii),  a  U.S.  Fish  and  Wildlife  Service  species  of  special  concern  (Harvey 
et  al   1999) 

Gates  were  installed  to  allow  for  continued  use  of  each  mine  working  by  bats  while 
prohibiting  accidental  livestock  entry  and  unauthorized  access  by  humans.  Gates  were  built  with 
13  mm  rebar  attached  to  an  angle  iron  gate  frame,  using  recommended  vetical  spacing  at  least 
5.75  inches  and  horizontal  spacing  at  least  24  inches  (Turtle  and  Taylor  1994,  Dalton  and  Dalton 
1995)  The  gate  itself  was  attached  to  a  corrugated  metal  pipe  that  was  inserted  into  the  mine 
portal,  surrounding  the  pipe  with  fill  to  assure  that  entry  into  the  mine  was  through  the  pipe  and 
gate,  the  gate  was  secured  with  a  protected  padlock    Although  the  gate  design  was  supposed  to 
be  bat-friendly,  no  follow-up  study  had  been  conducted  at  any  of  the  sites  to  determine  if  bats 
were  still  using  the  sites  after  gates  were  in  place 

The  objectives  of  the  work  described  in  this  report  were  two-fold.  First,  determine  the 
effectiveness  of  the  gate  design  in  its  primary  function  of  allowing  continued  access  by  bats  to 
the  mine  workings    Second,  gather  mine  environment  data  (temperature,  relative  humidity) 
continuously  over  a  several  month  period  to  aid  in  characterization  of  the  mine  environments 
where  bats  occurred 


STUDY  SITES  AND  METHODS 

The  McDonald  ("Ravalli")  Mine  is  just  west  of  the  small  community  of  Ravalli,  in  Lake 
County.  T18NR20WS3  1NWNE  at  about  853  m  (2800  ft)  elevation  near  the  Jocko  River  and  at 
the  southern  boundary  of  the  National  Bison  Range    The  mine  includes  three  open  adits  that 
produced  crude  copper  ore,  the  lower  two  of  which  are  now  gated    The  mine  has  not  been 
worked  since  1917  (Rossillon  1995) 

The  Gypsum  Mine  lies  within  the  boundary  of  Lewis  and  Clark  Caverns  State  Park,  in 
Jefferson  County,  about  275-305  m  (900-1000  ft)  elevation  below  the  mouth  of  the  cave,  and 
overlooking  the  Jefferson  River    The  mine  is  part  of  a  1 18-acre  claim  patented  in  1915  that 
includes  a  number  of  prospects,  a  large  open  pit,  and  a  couple  of  adits    The  two  gated  adits  are 
in  T1NR2W  in  S21NWNW  (adit  #1)  and  S20NENE  (adit  #2),  at  about  1432  m  (4700  ft)  and 
1390  m  (4560  ft)  elevation,  respectively 

During  mine  surveys,  all  bats  encountered  were  recorded  and  identified  to  species,  if 
possible,  taking  care  not  to  disturb  the  bats    Location  of  bats  within  the  mine  was  noted,  and  a 
series  of  temperature  and  relative  humidity  measurements  were  made  with  a  Bacharach  sling 
psychrometer    Mines  were  explored  to  the  fullest  extent  possible,  which  depended  in  part  on 
underground  configuration  and  relative  hazard    At  least  one  electronic  data  logger  (HOBO, 
Onset  Computer  Corporation,  Bourne.  MA)  was  installed  in  each  working,  usually  within  the 
area  occupied  by  bats    Data  loggers,  set  to  record  temperature  and  relative  humidity  every  6 


hours,  were  attached  to  extendable  aluminum  poles  (Mr.  Longarm,  Inc.,  Greenwood,  MO)  using 
duct  tape,  and  positioned  to  within  40  cm  of  the  ceiling  (ca.  1.4  to  2.0  m  above  ground). 
Location  of  data  loggers  relative  to  portals  was  documented;  data  loggers  were  left  in  mines  for 
6-7  months  before  retrieval.  Data  loggers  in  the  McDonald  Mine  adits  were  installed  on  7 
December  1998  and  retrieved  on  13  July  1999.  At  the  Gypsum  Mine,  data  loggers  were  installed 
on  6  January  1999  and  retrieved  13  July  1999.  Summary  Figures  portraying  data  logger  results 
are  presented  at  the  end  of  this  report. 


RESULTS 

McDonald  Mine  Sites.  On  7  December  (13: 10-16:30  MST),  the  two  (east  and  west)  gated  adits 
were  entered  and  data  loggers  installed.  In  the  East  Adit,  8  hibernating  Townsend's  Big-eared 
Bats  (Corynorhinus  townsendii)  were  found  on  the  walls  of  the  entrance  hallway  in  the  first  39.7 
m  (130  ft)  beyond  the  gate.  A  data  logger  ("shallow")  was  placed  at  this  point  39.7  m  from  the 
portal,  where  the  main  passage  angles  sharply  to  the  west  (left).  A  second  data  logger  ("deep") 
was  placed  106.7  m  (350  ft)  from  the  portal  in  this  west-trending  passage,  shortly  before  the 
workings  open  into  a  large  room  ascending  to  at  least  one  additional  level.  No  bats  were  found 
in  this  section  of  the  mine  on  the  December  survey,  and  the  second  level  beyond  the  large  room 
were  not  checked.  On  the  1 3  July  survey,  a  single  unidentified  Myotis  flew  from  the  entrance 
when  it  was  entered  (08: 17)  but  no  additional  bats  were  present  in  the  first  part  of  the  mine.  One 
Townsend's  Big-eared  Bat  was  seen  flying  in  the  upper  parts  of  the  large  room.  It  is  possible 
other  bats  were  present  in  this  portion  of  the  mine. 

In  the  West  Adit  no  bats  were  found  during  the  7  December  survey.  This  working  was 
surveyed  entirely  (about  50  m;  164  ft),  and  a  data  logger  was  left  where  the  main  haulway  angles 
sharply  to  the  east,  12.7  m  (41.7  ft)  from  the  entrance.  On  the  13  July  survey,  a  single 
Townsend's  Big-eared  Bat  flew  from  the  entrance  area  and  a  nursery  colony  of  20-25  individuals 
was  found  clustered  tightly  on  the  wall  of  the  east-trending  passage  near  its  juncture  with  the 
entrance  passage,  about  2.0  m  (6  5  ft)  beyond  the  data  logger. 

The  upper  ungated  adit  was  surveyed  on  7  December;  no  bats  were  found.  The  working 
is  relatively  shallow,  extending  17.1m  (56  ft)  beyond  the  portal. 

Climate  data  from  the  lower  gated  adits  (Table  1,  Figures  1-6)  show  all  workings  were 
relatively  cool  during  the  recording  period  (8  December  1998  to  13  July  1999).  Temperature 

TABLE  1.  Maximum  and  minimum  electronic  data  logger  values  for  temperature  (°C)  and  relative 
humidity  (RH;  %)  at  the  McDonald  Mine  sacs  (8  December  1998  to  13  July  1999)  and  Gypsum  Mine  sites  (7 
January  1999  to  13  July  1999). 


Mine  Working 

Ele\   (m) 

Max.  Temp 

Min.  Temp. 

Max.  RH 

Min.  RH 

McDonald  East  (shallow) 

853 

11.1 

-0.2 

100 

28.1 

McDonald  East  (deep) 

853 

11.9 

7.9 

100 

89.5 

McDonald  West 

853 

15.0 

9.1 

97.8 

59.0 

Gypsum  #1  (upper) 

1432 

~ 

- 

- 

- 

Gypsum  #2  (lower) 

1390 

7.1 

0.3 

989 

71.1 

varied  by  12°C  (20°F)  39.7  m  from  the  portal  in  the  East  Adit  during  this  period.  The  range  was 
6°C  (10.4°F)  12.7  m  from  the  portal  in  the  West  Adit,  and  only  3.5°C  (6.1°F)  deep  in  the  East 


Adit  106  7  m  from  the  portal    Maximum  temperatures  were  recorded  during  the  first  two  weeks 
of  July  in  each  adit,  minimum  temperatures  were  recorded  on  21-22  December  1998  (see  Figures 
1.  3,  5)    The  pattern  of  variation  in  relative  humidity  among  adits  was  identical  to  the  pattern  for 
temperature    Relative  humidity  varied  by  81  9%  at  the  shallow  location  in  the  East  Adit  (Figure 
2).  but  only  by  10 .5° o  at  the  deep  location  (Figure  4,  Table  1 )    In  the  West  Adit,  relative 
humidity  varied  by  38.8%  during  the  sample  period  (Figure  6)    Maximum  values  occurred  on  a 
range  of  dates  in  each  adit,  from  29  January  until  July  deep  in  the  West  Adit  and  between  5  May 
and  July  shallow  in  the  same  adit,  to  a  shorter  period  ( 1 8  June  to  6  July)  in  the  West  adit 
Minimum  relative  humidity  was  recorded  on  21  December  in  the  East  Adit,  but  on  13  July  in  the 
West  Adit 

Gypsum  Mine  Sites.  The  two  gated  Gypsum  Mine  adits  (#1   "upper"  and  #2  "lower")  were 
surveyed  completely  on  6  January  1999,  when  a  single  data  logger  was  installed  in  each    The 
upper  Adit  #1  extends  straight  back  for  22  4  m  (73.5  ft)  from  the  portal,  the  lower  Adit  #2 
extends  straight  back  for  44  0  m  ( 144  4  ft)    In  Adit  #1,  one  Townsend's  Big-eared  Bat  was 
hibernating  1  m  (3.3  ft)  above  the  floor  5  8  m  (19  0  ft)  from  the  drift  face.  In  Adit  #2,  one 
unidentified  Myotis  (probably  the  Little  Brown  Bat  A/,  lucifugus)  was  found  hibernating  wedged 
in  a  crack  about  5  0  m  (16.5  ft)  from  the  portal,  four  Townsend's  Big-eared  Bats  were 
hibernating  between  3  4  and  8.0  m  (1 1.2  and  26  2  ft)  from  the  portal    Three  additional 
Townsend's  Big-eared  Bats  were  hibernating  about  25  5  m  (83  7  ft)  from  the  portal    No  bats 
were  observed  in  either  adit  when  data  loggers  were  retrieved  on  13  July  1999 

In  Adit  n\  a  data  logger  was  installed  where  the  lone  bat  was  hibernating  5  8m  from  the 
drift  face    Unfortunately,  this  data  logger  failed  to  record  any  data  during  the  recording  period  (7 
January  to  13  July  1999)    However,  at  the  time  the  data  logger  was  installed,  temperature  in  this 
adit  ranged  from  3.9-6  4°C  (39-43  5°F),  the  warmest  value  about  3  m  (9  8  ft)  from  the  drift  face, 
relative  humidity  was  53%  1 2  6  m  (4 1  3  ft)  from  the  portal  to  the  drift  face    In  Adit  #2  a  data 
logger  was  installed  8  m  (26.2  ft)  from  the  portal  (36  m  from  the  drift  face),  at  the  far  end  of  the 
primary  zone  of  bat  occupancy    At  this  location  mine  temperature  varied  by  6  8°C  (12  2°F)  in  6 
months,  relative  humidity  varied  by  27  8%  (Table  1 )    Maximum  temperature  and  relative 
humidity  (Table  1 ,  Figure  7  and  8,  respectively)  were  recorded  in  the  first  part  of  July,  just  prior 
to  data  logger  retrieval,  minimum  values  for  each  variable  were  recorded  on  24  January 


DISCUSSION 

Workings  at  both  mine  sites  were  gated  because  they  were  known  to  harbor  bats  in 
winter    Townsend's  Big-eared  Bat  (( 'orynorhmus  townsendii)  has  been  known  to  occupy  the 
McDonald  Mine  workings  since  at  least  1965  (specimens  UMZ9942  through  UMZ9945, 
collected  5-6  December,  P  L  Wright  Vertebrate  Museum,  University  of  Montana)    More 
recently  the  three  adits  of  this  mine  were  surveyed  on  6  November  1996    Five  hibernating 
Townsend's  Big-eared  bats  were  present  in  the  East  Adit  (20-61  m  from  the  portal)  and  another 
was  activelv  thing,  no  bats  were  present  in  the  West  Adit    One  fresh  dead  big-eared  bat  was 
found  in  the  upper  adit  as  was  one  active  individual,  probably  the  same  active  bat  in  the  East 
Adit    Use  of  the  Gypsum  Mine  adits  is  less  well-documented,  but  bat  activity  in  and  around 
Lewis  and  Clark  Caverns  has  been  reported  for  many  decades  (Lee  Flath,  pers  comm  ) 

The  surveys  reported  here  indicate  continued  use  of  all  gated  mine  workings  by  bats, 
certainly  an  encouraging  finding  that  indicates  the  gate  design  in  use  is.  indeed,  bat  friendly 


Furthermore,  the  number  of  bats  present  (8)  at  the  McDonald  Mine  adits  on  7  December  1998 
was  nearly  identical  to  the  number  (7)  found  in  the  same  portion  of  workings  surveyed  on  6 
November  1996,  just  prior  to  gate  installation.    This  further  supports  the  idea  that  the  gating  had 
little  impact  on  the  attractiveness  of  these  mine  workings  to  bats. 

The  West  Adit  of  the  McDonald  Mine  appears  to  be  used  mostly  as  a  maternity  site, 
whereas  the  East  Adit  is  used  as  a  hibernaculum.  The  West  Adit  was  warmest  with  the  least 
humidity,  both  of  which  promote  more  rapid  development  of  young  (Humphrey  and  Kunz  1976). 
The  McDonald  East  Adit  and  the  two  Gypsum  Mine  adits  provide  conditions  suitable  for  use  as 
hibernacula  by  Townsend's  Big-eared  Bat:  temperatures  <  10°C  but  above  freezing  with  high 
relative  humidity  (Table  1,  Figures  1-8).  High  relative  humidity  reduces  water  loss  and 
desiccation  while  bats  are  inactive,  low  temperature  reduces  metabolic  costs  and  use  of  fat  stores. 
The  temperature  values  are  similar  to  those  reported  for  big-eared  bat  hibernacula  in  northern 
California  (Pierson  et  al.  1991),  Idaho  (Genter  1986),  Kansas  (Twente  1955),  and  Oklahoma 
(Humprey  and  Kunz  1976),  but  not  as  warm  as  in  other  parts  of  its  range  (summary  in  Webb  et 
al.  1996). 


RECOMMENDATIONS 

1)  The  gate  design  at  the  McDonald  and  Gypsum  mines  is  bat  friendly  and  works.  Continue 
using  this  design  where  appropriate  at  other  adits  as  additional  abandoned  mines  are 
reclaimed. 

2)  Other  gate  designs  have  been  installed  by  the  state  on  abandoned  mine  workings  elsewhere  in 
Montana  that  are  not  effective  in  preventing  unauthorized  human  entry.  Some  of  these 
designs,  using  brick  walls  that  may  alter  airflow,  could  also  alter  mine  environments  and 
affect  their  suitability  as  hibernacula  or  maternity  roosts  (Richter  et  al.  1993).  Consider 
replacing  these  with  the  current  design,  especially  at  sites  where  use  by  bats  has  been 
documented. 

3)  Continue  monitoring  bat  use  at  the  McDonald  and  Gypsum  mines.  Both  sites  are  ideal  for 
long-term  monitoring  of  a  bat  species  of  special  concern,  and  provide  both  hibernacula  and 
maternity  roosts.  Monitoring  could  include  multiple  visits  (every  other  month)  by  qualified 
bat  biologists  to  document  timing  of  occupancy  and  location  in  each  working  throughout  the 
year;  special  care  must  be  taken  to  minimize  disturbance  of  bats  if  monitoring  is  done  this 
frequently.  However,  these  data  will  provide  a  better  understanding  of  roost  requirements 
that  may  help  determine  the  suitability  or  lack  of  suitability  of  other  abandoned  mines,  and 
aid  in  decisions  to  close  or  gate  other  sites. 


LITERATURE  CITED 

Dalton,  D.  C,  and  V.  M.  Dalton.   1995.  Mine  closure  methods  including  a  recommended  gate 
design.  Pp.  130-135  in  Riddle,  B.  R.  (ed).  Inactive  mines  as  bat  habitat:  guidelines  for 
research,  survey,  monitoring  and  mine  management  in  Nevada.  Biological  Resources 
Research  Center,  University  of  Nevado,  Reno. 

Genter,  D.  L.   1986.  Wintering  bats  of  the  Upper  Snake  River  Plain:  occurrence  in  lava-tube 
caves.  Great  Basin  Naturalist  46:241-244. 


Harvey,  M  J  ,  J  S  Altenbach,  and  T  L  Best  1999  Bats  of  the  United  States.  Arkansas  Game 
&  Fish  Commission,  and  the  U  S  Fish  and  Wildlife  Service    64  pp 

Humphrey,  S  R  ,  and  T  H  Kunz  1976  Ecology  of  a  Pleistocene  relict,  the  Western  Big-eared 
Bat  {Plecotus  townsendii),  in  the  southern  Great  Plains  Journal  of  Mammalogy  57:470- 
494 

Pierson,  E  D  ,  W  E  Rainey,  and  D  M  Koontz    1991    Bats  and  mines:  experimental  mitigation 
for  Townsend's  Big-eared  Bat  at  the  McLaughlin  Mine  in  California    Pp.  3 1-42  in 
Proceedings  V:  Issues  and  technology  in  the  management  of  impacted  wildlife    Thome 
Ecological  Institute,  Boulder,  CO. 

Rjchter,  A  R.,  S  R  Humphrey,  J  B  Cope,  and  V.  Brack,  Jr  1993  Modified  cave  entrances 
thermal  effect  on  body  mass  and  resulting  decline  of  endangered  Indiana  Bats  (Myotis 
sodalis)    Conservation  Biology  7:407-415 

Rossillon,  M.  1995.  The  McDonald  Mine,  west  of  Ravalli:  a  cultural  resource  inventory  and 
evaluation    Renewable  Technologies,  Inc.,  Butte,  MT.  Unpublished  report.  24  pp 

Tuttle,  M  D,  and  D  A.  R.  Taylor    1994    Bats  and  mines    Bat  Conservation  International 
Resource  Publication  Number  3    4 1  pp 

Twente,  J  W,  Jr.    1955.  Some  aspects  of  habitat  selection  and  other  behavior  of  cavern- 
dwelling  bats    Ecology  36:706-732. 

Webb,  P  I ,  J  R  Speakman,  and  P  A  Racey.  1996.  How  hot  is  a  hibernaculum9  A  review  of 
the  temperatures  at  which  bats  hibernate    Canadian  Journal  of  Zoology  74:761-765. 


02/06        03/08        04/07 

New  logger  S/M213620  TEMP/RH 


05/07 


06/06        07/06 
S/N  213620 


Figure  1.  Mine  temperature  of  the  McDonald  Mine  East  Adit  (shallow  location),  Lake  County, 
Montana,  from  December  1998-July  1999.  Electronic  data  recorder  was  39.7  m  from  the 
mine  portal. 


01/08 


02/07        03/09        04/08        05/08 
New  logger  S/H/213620  TEMP/RH   ... 


06/07        07/07 
S/N  213620 


Figure  2.  Relative  humidity  of  the  McDonald  Mine  East  Adit  (shallow  location),  Lake  County, 
Montana,  from  December  1998-July  1999.  Electronic  data  recorder  was  39.7  m  from  the 
mine  portal 


12/10 
1998 


01/09 


02/08        03/10        04/09 

New  logger  S/NS213613  TEMP/RH 


05/09 


06/08        07/06 
S/N  213613 


Figure  3.  Mine  temperature  of  the  McDonald  Mine  East  Adit  (deep  location),  Lake  County, 
Montana,  from  December  1998-July  1999.  Electronic  data  recorder  was  106.7  m  from 
the  mine  portal. 


05/07 


Hew  logger  S/N/213613  TEMP/RH 


~1 

06/06         07/06 
S/N  213613 


Figure  4    Relative  humidity  of  the  McDonald  Mine  East  Adit  (deep  location),  Lake  County, 
Montana,  from  December  1998-July  1999.  Electronic  data  recorder  was  106  7  m  from 
the  mine  portal 


02/08        03/10        04/09 

Hew  logger  S/N/213624  TEMP/RH 


05/09 


06/08        07/0E 
S/N  213624 


Figure  5.  Mine  temperature  of  the  McDonald  Mine  West  Adit,  Lake  County,  Montana,  from 
December  1998-July  1999.  Electronic  data  recorder  was  12.7  m  from  the  mine  portal. 


10 


12/09 
1998 


02/07        03/09        04/08 

Mew  logger  S/H/213624  TEMP/RH 


05/08 


06/07         07/07 
S/N  213624 


Figure  6    Relative  humidity  of  the  McDonald  Mine  West  Adit,  Lake  County,  Montana,  from 
December  1998-July  1999.  Electronic  data  recorder  was  12.7  m  from  the  mine  portal 


u 


03/10  04/09  05/09 

New  logger  S/M213604  TEMP/RH   ... 


06/08 


07/06 
S/N  213604 


Figure  7.  Mine  temperature  of  the  Gypsum  Mine  Adit  #2,  Jefferson  County,  Montana,  from 
January- July  1999.  Electronic  data  recorder  was  8.0  m  from  the  mine  portal. 


12 


01/08 
1999 


02/07 


03/09  04/08  05/08 

New  logger  S/N/213604  TEMP/RH   ... 


06/07  07/07 

S/N  213604 


Figure  8    Relative  humidity  of  the  Gypsum  Mine  Adit  #2,  Jefferson  County,  Montana,  from 
January-July  1999    Electronic  data  recorder  was  8  0  m  from  the  mine  portal 


13