2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...

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2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
M AINE NIGHTJA R
   MONITOR ING PROJECT

                              2021
MONITOR ING H ANDBOOK

                         A PROJ EC T OF T H E
            M A I N E NAT U R A L H I S TOR Y OB S E RVATOR Y

M A I N E N IGH T JA R.C OM           M A I N E NAT U R A L H IS T ORY.ORG
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
TABLE OF CONTENTS
 VOLU N T E E R                       R EQU IR E M E N T S                            ............................................................ . . . . . 1
 EQU I PM E N T                        ........................... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .......1
 T E R MS              AND             DE F I N I T IONS.......................................................................1
 W H E N T O SU RV E Y.................... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .......2
      I M POR TA N T R E M I N DE R S........................................................................4
      F OL LOW U P MO ON R I S E S U RV E Y S................................................... ......5
      I F YOU CA N ’ T C OM PL ET E YOU R S U RV E Y....................................... ......5
 ROU T E                LO GIS T IC S.............................................................................. ......5
        SU RV E Y FOR MS......................................................................................6
        R EC OR DI NG E N V I RON M E N TA L C ON DI T IONS......................................7
                         W I N D............. .............. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. ..................6
                         SK Y C ON DI T IONS......... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .......7
                          NOISE. . . . . . . . . . . . . . . . . . . . . . . . ..................................................................8
                          C A R S............................................................................................9
                         T E M PE R AT U R E............................................................................9
                         S TA R T T I M E................................................................................9
 C ON DUC T I NG T H E SU RV E YS...... .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .......9
       W H AT SPECI E S T O R EC OR D.. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. ......10
        SA M PL E DATA FOR M.. . . . . . . . . . . . .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. .. ......12
       C OM M E N T S.......................... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .....12
 DATA             SU BM IS SION ................................................................................ . . . . 12
 SA FET Y...................................................................................................12
 QU E S T IONS ? . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 2
 A PPE N DI X A: 2 02 1 SOL A R & LU NA R C A L E N DA R..................................... . . . . . 13
 A PPE N DI X B: H A BI TAT T Y PE S............................................................... . . . 14
 A PPE N DI X C: BR E E DI NG C ODE S...............................................................16

                       I N T RODUC T ION

Thank you for agreeing to participate in the
Maine Nightjar Monitoring Project. The primary
focus of this survey is to collect data on two species
of nightjars in Maine: Eastern Whip-poor-will
(Antrostomus vociferus) and Common Nighthawk
(Chordeiles minor). These difficult to study species
are thought to have declined severely in the past
50 years. In addition, we are asking volunteers to
collect data on owls as well as other nocturnal
and crepuscular bird species during their surveys.
These data will be used to track changes in
distribution and identify areas where these
species may still be relatively abundant and guide
land protection efforts, habitat management,
and future research and monitoring efforts.
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
VOLU N T E E R R EQU I R E M E N T S                                  EQU I P M E N T

This project relies on volunteers to conduct                             • DATA SHEETS
standardized surveys along roadside survey routes                        AND CLIPB O ARD
during specific conditions. The only experience
                                                                         • SURVEY
necessary is a familiarity with each species’
characteristic songs (Listen to examples at www.                         PRO TO CO L
mainenightjar.com on “The Birds We Study”                                • ROUTE MAP AN D
page). It will also be helpful to be familiar with                       CO O RDIN ATES
non-vocal sounds such as the “booming” display of
the Common Nighthawk.                                                    • FLASHLIGHT
                                                                         AND/OR
Volunteers need to conduct 2 surveys (1 moonrise                         H E ADLAMP
survey and 1 sunset survey) along pre-established
routes. All routes must be run between May 19 and                        • STO PWATCH /
June 2. In most instances, the moonrise survey can                       TIMER
immediately follow the sunset survey, but there
                                                                         • PENS/ PE N CILS
are exceptions. An additional moonrise survey
before mid-July will also be required if nightjars                       • GPS OR
were detected during the first round of surveys.                         SMARTPH O N E
Please read carefully and follow the instructions.
Compliance with these instructions will ensure                           • HAND-HELD
standardized data collection and a successful                            THERMOMETER
survey.                                                                  (O PTIO NAL)

                              T E R M S A N D DE F I N I T IONS

Survey Route
Survey routes are 9 miles long and are positioned throughout the state so that they pass through areas of
suitable nightjar habitat. They run along roadways so they can be safely accessed at dusk and after dark.

Sunset Survey
Sunset surveys target Nighthawks and other crepuscular species that are most likely to be found just
before or just after sunset. Sunset surveys should be timed to run approximately 45 minutes before to 45
minutes after sunset. Sunset surveys can be conducted at any date within the survey window, irrespective
of the lunar cycle.

Moonrise Survey
Moonrise surveys target Eastern Whip-poor-will and other night-calling bird species. Moonrise surveys
should start at least 15 minutes after sunset or end no later than 15 minutes before sunrise.

Lunar Cycle
A lunar cycle is a two-week period of time centered around the full moon when moonrise surveys may be
conducted. For 2021, the 1st lunar cycle is May 19 to June 2 and the 2nd lunar cycle is June 17 to July 1.

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              Maine Nightjar Monitoring Project - Maine Natural History Observatory
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
E A S T E R N W H I P-P O OR-W I L L

                                                                                     L O G A N P A RK E R

                                         W H E N TO S U RV E Y

      Nightjars are known to be more vocal around a full moon and relatively quiet when
      the moon is poorly illuminated or below the horizon. For this reason, sunset and
      moonrise surveys are restricted to the week leading up to and the week following the
      full moon. In addition, for moonrise surveys it is important to delay your survey (if
      needed) to allow the moon to rise above the horizon or to not be obscured by clouds.
      When scheduling a moonrise survey, keep in mind that the moon rises progressively
      later each night as it wanes (i.e., after the full moon) requiring you to stay up later into
      the night (or get up early) to start your survey. In most instances, the moonrise survey
      can immediately follow the sunset survey as long as the moon is visible (i.e., above the
      horizon and not blocked by clouds).

      When scheduling your survey, the arrival date of Maine nightjars, the date of the full
      moon, and weather conditions must all be taken into consideration as follows:

      Step 1
      Look at table 1 below and find the start and end date of your survey period based on the
      location of the route.

           TA BL E 1. L AT I T U DI NA L VA R I AT ION I N A R R I VA L DAT E S

              N IGH T JA R             LOC AT IONS               S TA R T OF           E N D OF

            A R R I VA L DAT E                                SU RV E Y PE R IOD   SU RV E Y PE R IOD

                 M AY 1            SOU T H E R N M A I N E         M AY 15             J U N E 30

                                 (SOU T H OF AUG US TA )
                M AY 10            NOR T H E R N M A I N E         M AY 25             J U LY 15

                                 (NOR T H OF AUG US TA )

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                     Maine Nightjar Monitoring Project - Maine Natural History Observatory
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
Step 2
 Compare the information you found in table 1 with table 2. Your survey window is
 the period of time that falls within the 1st lunar cycle and within the survey period
 you looked up in table 1.

 TA BL E 2. ACC E P TA BL E S U RV E Y W I N D OWS B A S E D ON LU NA R
 PH A S E F OR 2 0 2 1 . I N T H I S TA BL E , T H E F U L L MO ON OCC U R S
 ON T H E L A S T DAY OF T H E WA X I NG MO ON .

             LU NA R PH A SE             1S T C YCL E              2N D C YCL E

             WA X I NG MOON           M AY 19 - M AY 2 6       J U N E 17 - J U N E 2 4

             WA N I NG MOON           M AY 27 - J U N E 2       J U N E 25 - J U LY 1

Step 3
Look at Appendix A on page 13 to narrow down when to attempt your survey(s). When
planning, remember that (1) sunset surveys should start 45 minutes prior to sunset, and
(2) moonrise survey should start at least 15 minutes after sunset and end no later than
15 minutes before sunrise. Consider making a backup plan as there is always a chance
weather conditions will make it necessary to postpone a survey.

Step 4
As your survey window approaches, start watching the weather. Sunset and moonrise
surveys can only be run when the lunar and sky conditions are suitable, as follows:

• Sunset surveys cannot be conducted when wind is a 3 or higher on the Beaufort Scale
and during drizzle, rain, or snow. (see Beaufort Scale table on page 5).

• Moonrise surveys cannot be conducted when wind is a 3 or higher on the Beaufort
Scale and during drizzle, rain, snow, or any conditions (such as cloud or fog) which
would obscure the moon for more than 3 stops. (see Beaufort Scale table on page 5).

C OM MON N IGH T H AW K

                                                                            L O G A N P A RK E R
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              Maine Nightjar Monitoring Project - Maine Natural History Observatory
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
I M P ORTA N T R E M I N DE R S

    •     All routes must be run during the 1st lunar cycle (May 19 to June 2).
    •     The sunset survey should be timed to run approximately 45 minutes before to 45
          minutes after sunset.
    •     Begin each moonrise survey at least 15 minutes after sunset and end no later than
          15 minutes before sunrise.
    •     Moonrise surveys must be conducted when the moon is in the sky and not
          obstructed by fog or clouds.
    •     If conditions do not allow for running the moonrise survey on the same evening
          as the sunset survey, run the moonrise portion of the survey on the next possible
          evening.

    Note that the moon rises later each evening during these survey periods, and that by the
    end of the period a pre-dawn survey would be required.

    In such cases be sure to leave roughly 1.5 hours to complete the survey so that it ends
    before sunrise. It is CRITICAL that surveys are conducted during appropriate lunar
    conditions, irrespective of the date within the survey period.

    A table detailing sunrise, sunset, moonrise, and moonset can be found in Appendix A
    (page 13).

E A S T E R N W H I P-P O OR-W I L L

                                                                                  JOH N W I N Z E

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                Maine Nightjar Monitoring Project - Maine Natural History Observatory
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
F OL LOW U P MO ON R I S E S U RV E Y S

Southern Maine: If a nightjar is detected along a route in southern Maine during the first
lunar cycle (May 19 – June 2), the route will need to be re-run 7 or more days later during
the 1st lunar cycle or early during the 2nd lunar cycle (June 17 – June 30) to document
the level of confidence that nightjars are breeding along the route.

Northern Maine: If a nightjar is detected along a route in northern Maine during the
first lunar cycle (May 25 – June 2), the route will need to be re-run during the 2nd lunar
cycle (June 17 – July 1) to document the level of confidence that nightjars are breeding
along the route. Sunset surveys do not need to be re-run.

If you are unable to re-run your moonrise survey(s) during the 2nd lunar
cycle, contact Logan Parker (logan@hereinthewild.com).

                 I F YOU CA N ’ T C OM PL ET E YOU R S U RV E Y

The Maine Nightjar Monitoring Project is a long-term monitoring effort. As such, it is
essential that sunset and moonrise surveys are completed every year. If, for any reason,
you are unable to complete your survey in a given year, it is important to contact the
project coordinator as soon as possible to secure a substitute volunteer to cover your route.
Contact project coordinator Logan Parker at logan@hereinthewild.com.

                                 ROU T E LO GI S T IC S

The starting point for all surveys is stop number 1. All other stops are spaced approximately
1 mile apart along the route as indicated on your map (follow the UTM coordinates
provided for each point).

If the one-mile mark places you in a location that is not conducive to the survey (no
place to pull off, excessive highway noise, barking dogs, directly in front of a home, or
an otherwise unsafe location), you may continue on for up to 0.2 miles (note this in the
comment section and record the UTM location where you conducted your survey).

Be sure to continue to the exact UTM coordinate for the next point. Please be sure to
follow any instructions that accompany the provided map in such cases.

If you are having trouble locating your route, contact the project coordinator so they can
help you with directions. It is important you do this as soon as possible to ensure that the
route is running during the 1st lunar cycle.

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             Maine Nightjar Monitoring Project - Maine Natural History Observatory
2021 MAINE NIGHTJAR MONITORING PROJECT - MONITORING HANDBOOK A PROJ ECT OF TH E - Maine Natural History ...
S U RV E Y F OR M S

    There are three survey forms that will need to be completed during the first run of the
    route (during the 1st lunar cycle): the Sunset Survey Form (page 11), the Moonrise Survey
    Form (page 12), and the Survey Route Description form (page 10). The instructions
    below outline the tables found on the survey forms. Please report data as accurately
    and completely as possible. You may want to conduct a test run on a date prior to your
    scheduled surveys so as to become familiar with the census techniques and the form.

    Survey Route Description Form: This form is used to gather data about habitat conditions
    along your survey route. It should be completed prior to your survey efforts at a time when
    habitat conditions are easily discernable. At each point, provide a general description of
    the point (visible within 100 meters), a count of the number of houses or other buildings,
    and the top 3 most dominant habitat types at the point. Habitat codes are listed at the
    bottom of the Survey Route Description Form. A more thorough explanation of habitat
    types can be found in Appendix B (page 14).

    Sunset and Moonrise Survey Forms: Both of these forms have the same format and use
    the same wind, sky condition, and noise data detailed in the tables below. Observation
    data should be entered on the survey form during their respective survey; however,
    environmental conditions should be noted at the point before commencing with your
    observations. Do not wait to enter your observation data until after the survey effort to
    avoid potential errors of omission.

    Route Name: This should be on the map you receive from your coordinator.
    Observer: Record your name here.
    Date: Indicate the date of the survey.
    Time Start: Indicate the time at which you begin listening at stop 1.
    Time End: Indicate the time at which you stop listening at stop 10.

CH UC K - W I L L’ S-W I D OW

                                                                                    M A RY A L IC E
                                                                                         TAT L E R

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                 Maine Nightjar Monitoring Project - Maine Natural History Observatory
R EC OR DI NG E N V I RON M E N TA L C ON DI T IONS

For each point, we ask that you give an indication of the following environmental
conditions. Use only the code systems detailed below. It is important to conduct surveys
only under appropriate environmental conditions to ensure birds can be detected. Sunset
surveys cannot be conducted when wind is a 3 or higher on the Beaufort Scale and during
drizzle, rain, or snow. Moonrise surveys cannot be conducted when wind is a 3 or higher
on the Beaufort Scale and during drizzle, rain, snow, or any conditions (such as cloud or
fog) which would obscure the moon for more than 3 stops.

Wind: Record the rough wind speed at each stop using the Beaufort codes below. Do not
begin a survey if wind is a 3 or above on the Beaufort Scale. If wind intensifies during the
survey, and winds of a Gentle Breeze (3) or above persist for more than three stops, end
the survey and attempt it again under better conditions.

BE AU FOR T         WIND      DE SCR I P T ION
N U M BE R          SPE E D
        0
LO GAN PARK ER

    Noise: Assign a noise code to each stop. Noise codes are a measure of the effect of noise
    on your ability to hear vocalizing birds. Although we have provided examples of noises
    for each code, these are meant only as general guidelines.

    C ODE        DE SCR I P T ION

         0       T H E R E IS NO A PPR ECI A BL E E F F EC T ON YOU R A BI L I T Y T O H E A R
                 BIR DS.
         1       NOISE SL IGH T LY A F F EC T S YOU R A BI L I T Y T O H E A R BIR DS (E.G.
                 DIS TA N T TR A F F IC, D O G B A R K I NG, 1 - 2
                 C A R PA S SI NG DU R I NG SU RV E Y PE R IOD).
         2       NOISE MODE R AT E LY A F F EC T S YOU R A BI L I T Y T O H E A R BIR DS ( E.G.
                 N E A R BY   TR A F F IC,   3-6   CARS      PA S SI NG   DU R I NG   S U RV E Y   PE R IOD,
                 A IR PL A N E F LY I NG OV E R H E A D ).

         3       NOISE SE R IOUSLY A F F EC T S YOU R A BI L I T Y T O H E A R BIR DS (E.G.
                 C ON T I N UOUS TR A F F IC N E A R BY, C ONS TRUC T ION NOISE, LOU D SPR I NG
                 PE E PE R C HORUS )

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                 Maine Nightjar Monitoring Project - Maine Natural History Observatory
Cars: Record the number of cars that pass by during each of the entire count periods as
a rough index of traffic noise. Counting cars is not the primary objective of the survey,
however. Cap your car counting effort at 15 cars and record it on the data sheet as “15+”.
Rather than counting a high number of cars, focus your energy on listening for what
vocalizations you can discern through the traffic noise or breaks in traffic.

Temperature: Record the air temperature in Fahrenheit at each stop at the beginning
of each survey. The most accurate means of recording temperature would be to utilize a
handheld thermometer, however, if you do not have access to such a device, your car’s
built-in thermometer or local weather application will suffice.

Start Time: Record the time you start your observations at each point.

                          C ON DUC T I NG T H E S U RV E Y

While a single observer can conduct these surveys on their own, volunteers are welcome
to bring a partner to assist with the survey efforts. Only one volunteer should count and
record the birds detected. The other partner can act as the designated timekeeper and
can announce the start of the survey and the break between the one-minute periods.

At each point, the observer will spend six minutes listening for nightjars and other
vocalizing birds, with each bird’s detections tracked across one-minute periods. What
this means in practice is that you will have a single line on the survey form for each
individual bird detected (see example on the following page) and you will mark whether
you detect it in each of the six one-minute periods. Additionally, we are asking that
volunteers report the highest level of breeding behavior observed. Given that much of
the survey effort will be completed near or after sunset, birds will likely be more often
heard than seen. Consequently, “Singing Male” will often be the highest level detected.
A more detailed explanation of breeding codes can be found in Appendix C (page 16).

•   Birds will sometimes move during the count, and you will need to use your best
    judgment when deciding if a “new” detection is actually an additional bird or simply
    an already-counted bird that has moved its location.

•   Listening and recording data should be done from a safe, stationary point outside the
    car.

•   Do not use whistling, playbacks, or any other method of coaxing birds to vocalize or
    move. Record birds detected during only the six-minute sample period, although you
    may record birds detected outside of this period in the “Comments” section of the
    form.

•   Record birds as you hear them, rather than waiting for the sample period to be over,
    so as to avoid errors of omission.

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             Maine Nightjar Monitoring Project - Maine Natural History Observatory
W H AT S P ECI E S TO R EC OR D

     While the birds listed below are the most likely to be observed, this list in not exhaustive
     and all observed species that can be confidently identified should be reported:

     Nightjars:                                        Owls:
                                                       Owls:
     Eastern Whip-poor-will                            Eastern Screech Owl
     Common Nighthawk                                  Great Horned Owl
     Chuck-will’s-widow**                              Barred Owl
                                                       Long-eared Owl**
                                                       Short-eared Owl**
                                                       Northern Saw-whet Owl

     Other Nocturnal/Crepuscular species:
                                  species:             Chimney Swift
     Common Loon                                       Veery
     Black-crowned Night-heron                         Swainson’s Thrush
     Yellow-crowned Night-heron**                      Hermit Thrush
     Yellow Rail**                                     Wood Thrush
     American Woodcock                                 American Robin
     Wilson’s Snipe                                    Northern Mockingbird
     Killdeer                                          Ovenbird

     *These species are rare in Maine and require additional documentation. Please take
     additional descriptive notes, photographs, video, and/or audio recordings when possible.

     If a bird that is not listed above is observed, write out the species name. Abbreviations are
     acceptable so long as they are easily recognized (e.g. “tree swal” for Tree Swallow). If
     no birds are detected at a point, enter the point number as usual, followed by “NONE”
     instead of a species code, and leave the columns for each time period blank (or draw a
     line through them). Doing so will reduce the possibility of becoming confused during a
     survey and forgetting which point you are on.

BARR ED
OW L

                                                                                 L O G A N P A RK E R

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                  Maine Nightjar Monitoring Project - Maine Natural History Observatory
S A M PL E DATA SH E ET

SU RV E Y              SPECI E S                      SU RV E Y M I N U T E       MOV E D ?   DIR.   BR E E DI NG

POI N T                                           1   2     3      4      5   6                        C ODE
    1       E A S T E R N W H I P-PO OR-W I L L   1   1     1      1      1   1               NE          S

    1       E A S T E R N W H I P-PO OR-W I L L   0   0     1      1      1   0                S          S

    2       NON E

    3       E A S T E R N W H I P-PO OR-W I L L   1   1     1      0     0    0                W          S

    3       E A S T E R N W H I P-PO OR-W I L L   0   0     0      1      1   1      X        SW          S

    3       C OM MON N IGH T H AW K               0   0     0      0      1   0                SE         C

    3       E A S T E R N W H I P-PO OR-W I L L   0   0     0      0      1   1                N          S

   4        B A R R E D OW L                      1   1     1      0     0    0                E          S

   4        E A S T E R N W H I P-PO OR-W I L L   0   0     0      1      1   1                SE         S

    5       ETC.

Example: In this form a “0” indicates that a given individual was NOT detected, while
a “1” indicates it was. For example, at Point 1 an Eastern Whip-poor-will was heard in
the first one-minute period and every period thereafter. A second Eastern Whip-poor-
will was first detected in the third period and heard in the following two periods before
becoming silent. No nightjars were heard at Point 2. At Point 3 an Eastern Whip-poor-
will was heard during the first three periods, changed location, and continued to sing
from that new location. Note that the “Moved?” column is used to document an individual
changing position and resuming its vocalizations. It is not used to indicate that a bird
is actively foraging or flying. A different Eastern Whip-poor-will was first detected in
Period 4 and heard again in Periods 5 and 6. Because it did not overlap with the first
bird, there is a possibility that they are the same bird and that it moved between Periods
3 and 4. Some cues that might suggest this are if calling ended early in Period 3 and
started late in Period 4, but there is no hard and fast rule. Use your best judgment and be
conservative about adding new individuals. Also at Point 3, both a Common Nighthawk
and an Eastern Whip-poor-will were detected in Period 5, with the latter continuing
into Period 6. The fact that this bird overlapped with the second Eastern Whip-poor-
will is clear evidence that there are at least two Eastern Whip-poor-wills at this point.
At Point 4, a Barred Owl was heard in Periods 1-3 and an Eastern Whip-poor-will in
Periods 2-6. This process would continue through Points 5-10.

Remember that each bird has its own line. Do not record two birds
calling from the same direction with a “2”.

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                   Maine Nightjar Monitoring Project - Maine Natural History Observatory
Comments: Use this field to provide any additional information not included in the table.

     For example:
     • other nocturnal species detected outside the observation period.
     • details on noise factors that might impede your ability to detect birds (use only if you
            used Noise Code 3 on a given point).
     • identification details of any rare or unusual species (Chuck-will’s-widow, Long-eared
            Owl, etc.) seen or heard during or following the survey period.
     • any other information you wish to convey.
     • if you need extra space, please feel free to write on the back of the forms.

                                      DATA S U BM I S SION

     Want to assist with entering project data? Data entry is another great way to help sustain
     the project. For more directions and to download the data entry spreadsheet, visit
     mainenightjar.com and go to the “Data Submission” page (under the “Volunteer” tab).
     Completed spreadsheets can be uploaded to the project site. Original data sheets should
     be sent to logan@hereinthewild.com.

                                              S A F ET Y

     Your safety comes first. Please ensure that you are conscious of your safety when
     conducting a survey.
     Please take the following points into consideration:
     • Consider conducting surveys in a team of two (with only one team member making
     observations).
     • If surveying alone, make sure someone knows where your survey route is and what time
     you will return.
     • Park your vehicle well off the road during survey stops.
     • Leave parking lights on throughout the duration of a count.
     • Wear a reflective vest and/or use a headlamp so that other drivers are aware of your
     location.
     • Conduct the survey near the road to avoid trespassing on private property.
     • Check your clothing and skin for ticks when you get home to prevent the transmission
     of Lyme disease and other tick-borne illnesses.
     • Consider notifying the local police/sheriff ’s department that you will be in the area
     conducting surveys after dark.

                                          QU E S T IONS ?

     Please contact the Project Coordinator, Logan Parker, for assistance.
     logan@hereinthewild.com - (207) 649-4689

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                  Maine Nightjar Monitoring Project - Maine Natural History Observatory
A P P E N DI X A. 2 0 2 1 S OL A R A N D LU NA R CA L E N DA R

W I N D OW                     DAT E         MOON R ISE        MOONSE T         SU N R ISE       SU NSE T
                               M AY 19          11 : 4 1 A M      1: 5 1 A M      5:08 A M            8: 01 PM
                               M AY 2 0         12: 5 3 PM        2: 19 A M       5:07 A M            8: 02 PM
     1 S T LU NA R C YCL E

                               M AY 2 1         2: 0 6 PM        2: 4 4 A M       5:06 A M            8: 03 PM
                               M AY 2 2         3: 2 2 PM         3:08 A M        5 : 05 A M          8: 04 PM
                               M AY 2 3         4: 4 1 PM         3:32 A M        5 : 04 A M          8: 05 PM
                               M AY 2 4         6 : 02 PM         3:5 7 A M       5 : 03 A M          8: 0 6 PM
                               M AY 25          7: 2 6 PM         4: 27 A M       5 : 02 A M          8: 0 7 PM
                               M AY 2 6         8: 4 8 PM         5 : 03 A M      5 : 01 A M          8: 0 8 PM
                               M AY 27         10:05 PM           5 : 47 A M      5 : 01 A M          8: 0 9 PM
                               M AY 2 8         11 : 11 PM        6: 5 2 A M      5:00 A M            8: 10 PM
                               M AY 2 9                           7 : 47 A M      4: 5 9 A M          8: 11 PM
                               M AY 30         12: 04 A M         8: 5 8 A M      4: 5 9 A M          8: 12 PM
                               M AY 31         12: 45 A M        10: 11 A M       4: 5 8 A M          8: 12 PM
                               JUNE 1           1 : 17 A M       11:2 3 A M       4: 5 7 A M          8: 13 PM
                               JUNE 2           1: 4 3 A M       12: 31 PM        4: 5 7 A M          8: 14 PM

 W I N D OW                    DAT E         MOON R ISE         MOONSE T         SU N R ISE       SU NSE T
                               J U N E 17       11: 5 2 A M       12: 4 9 A M      4: 54 A M           8: 2 3 PM
                               J U N E 18        1: 04 PM          1: 12 A M       4: 54 A M           8: 2 3 PM
      2 N D LU NA R C YCL E

                               J U N E 19        2: 19 PM         1: 34 A M        4: 54 A M          8: 2 4 PM
                               JUNE 20           3: 36 PM         1: 5 8 A M       4: 54 A M          8: 2 4 PM
                               JUNE 21          4: 5 6 PM         2: 34 A M        4: 54 A M          8: 2 4 PM
                               JUNE 22           6 : 18 PM        2: 5 6 A M       4: 54 A M          8: 2 4 PM
                               JUNE 23           7: 38 PM          3:3 5 A M       4: 5 5 A M         8: 2 4 PM
                               JUNE 2 4          8: 5 1 PM        4: 2 4 A M       4: 5 5 A M          8: 25 PM
                               J U N E 25        9 : 5 1 PM       5 : 25 A M       4: 5 5 A M          8: 25 PM
                               JUNE 26          10:3 9 PM         6: 3 5 A M       4: 5 6 A M          8: 25 PM
                               J U N E 27       11: 15 PM         7:49 A M         4: 5 6 A M          8: 25 PM
                               JUNE 2 8         11 : 45 PM        9: 04 A M        4: 5 6 A M          8: 25 PM
                               JUNE 29                            10: 16 A M       4: 5 7 A M          8: 25 PM
                               J U N E 30       12: 0 9 A M       11:2 4 A M       4: 5 7 A M         8: 2 4 PM
                               J U LY 1         12: 30 A M        12: 30 PM        4: 5 8 A M         8: 2 4 PM

                                                                                                                   13
                              Maine Nightjar Monitoring Project - Maine Natural History Observatory
A P P E N DI X B. L A N D C OV E R/H A BI TAT S V I SI BL E W I T H I N 10 0 M F ROM P OI N T.
 M ACRO - H A BI TAT            M ICRO -H A BI TAT                 DE SCR I P T ION
 DE V E LOPE D                  C OM M E RCI A L -                 DE V E LOPE D A R E A S W H E R E PEOPL E R E SI DE OR WOR K I N H IGH N U M BE R. E X A M PL E S I NCLU DE
 ( M I X OF I M PE RV IOUS      I N DUS TR I A L (> 8 0%           A PA R T M E N T C OM PL E X E S, ROW HOUSE S, C OM M E RCI A L-I N DUS TR I A L A R E A S, A N D A S SOCI AT E D
 S U R FAC E S A N D            I M PE RV IOUS )                   PA R K I NG. I M PE RV IOUS SU R FAC E S AC C OU N T FOR MOR E T H A N 8 0% OF T OTA L C OV E R.
 M A NAGE D L AW N
 GR A S SE S)                   H IGH I N T E NSI T Y (5 0-        I NCLU DE S H IGH LY DE V E LOPE D A R E A S W I T H A M I X T U R E OF C ONS TRUC T E D M AT E R I A L S A N D
                                8 0 % I M PE RV IOUS )             V EGE TAT ION. I M PE RV IOUS SU R FAC E S AC C OU N T FOR 5 0 T O 8 0 PE RC E N T OF T OTA L C OV E R .

                                M E DI U M I N T E NSI T Y         I NCLU DE S MODE R AT E LY DE V E LOPE D A R E A S W I T H A M I X T U R E OF C ONS TRUC T E D M AT E R I A L S
                                (2 0-5 0% I M PE RV IOUS)          A N D V EGE TAT ION . I M PE RV IOUS S U R FAC E S AC C OU N T FOR 2 0 T O 5 0 PE RC E N T OF T OTA L C OV E R .

                                LOW I N T E NSI T Y                I NCLU DE S SPA R SE LY DE V E LOPE D A R E A S W I T H A M I X T U R E OF C ONS TRUC T E D M AT E R I A L S
                                (8 0 % OF V EGE TAT ION C OV E R) A N D
 LOW H E R B S (GR A S SE S     GR A S SL A N D                    OC C A SIONA L LY SPA R SE TR E E S OR SHRU B S. T H E SE A R E A S A R E NOT SU BJ EC T T O I N T E NSI V E
 GE N E R A L LY >8 0%,                                            M A NAGE M E N T SUC H A S T I L L I NG, BU T M IGH T BE USE D FOR GR A Z I NG OR H AY PRODUC T ION
 W I T HOU T E V I DE NC E                                         BU T T H E R E A R E NO OBV IOUS OR R EC E N T SIGNS OF F E NCI NG A N D H AY I NG. C H A R AC T E R IS T IC
 OF R EC E N T PA S T U R E /                                      L A N D C OV E R F E AT U R E S: PR A IR I E S, DRY M E A D OW S, FA L LOW F I E L DS, A N D U N DE V E LOPE D
 H AY I NG)                                                        L A N DS W I T H NAT U R A L LY OC C U R R I NG GR A S SE S.

                                C OA S TA L GR A S SL A N DS /     GR A S SL A N DS A LONG M A R I N E C OA S T OR SHOR E S OF L A RGE L A K E S (TR E E S A N D SHRU B S
                                DU N E S                           SOM E T I M E S PR E SE N T BU T SU BOR DI NAT E T O SHRU B/GR A S S C OV E R), E.G., DU N E S, SA N DY
                                                                   A R E A S W I T H SPA R SE V EGE TAT ION A N D SM A L L PAT C H E S OF SHRU B S .

                                ROCK Y OU T CROP                   U PL A N D A R E A S A S SOCI AT E D W I T H ROCK OU T CROP S, LOW E L E VAT ION R I D GE S A N D SU M M I T S
                                GR A S SL A N D/GL A DE            W I T H A M I X T U R E OF GR A S SE S A N D LOW H E R B S.

 U PL A N D FOR E S T -         OA K- PI N E D OM I NA N T         OA K D OM I NAT E D W I T H SU BD OM I NA N T PI T C H PI N E, R E D PI N E, W H I T E PI N E, OR GR AY BIRC H,
 DECI DUOUS                                                        DE NSE T O OPE N WOODL A N DS W I T H A LOW SHRU B OR GR A S S L AY E R, OR W I T H SPA R SE C OV E R
 ( TR E E S USUA L LY                                              ON DRY ROCK Y H I L LT OP S A N D OU T CROP S . OV E R A L L TR E E S GR E AT E R T H A N 5 M TA L L A N D
 > 5 M TA L L A N D                                                GR E AT E R T H A N 75% DECI DUOUS .
 FOR E S T > 75%
                                R E D OA K- NOR T H E R N          A CLOSE D C A NOP Y FOR E S T OF LOW T O MODE R AT E MOIS T U R E I N W H IC H A SIGN IF IC A N T
 DECI DUOUS)
                                H A R DWOODS D OM I NA N T         C OM PON E N T OF R E D OA K IS PR E SE N T A LONG W I T H T H E NOR M A L SU I T E OF NOR T H E R N
                                                                   H A R DWOODS, PR I M A R I LY SUGA R M A PL E, BE EC H, A N D Y E L LOW BIRC H. R E D M A PL E, H E M LOCK,
                                                                   A N D W H I T E PI N E A R E C OM MON A S SOCI AT E S. OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D
                                                                   GR E AT E R T H A N 75% DECI DUOUS

                                BIRC H-BE EC H-M A PL E            NOR T H E R N H A R DWOODS SUC H A S SUGA R M A PL E, Y E L LOW BIRC H, A N D BE EC H A R E
                                D OM I NA N T                      C H A R AC T E R IS T IC, E I T H E R FOR M I NG A DECI DUOUS C A NOP Y OR M I X E D W I T H R E D OA K OR
                                                                   H E M LOCK (OR I N SOM E C A SE S W H I T E PI N E). OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D
                                                                   GR E AT E R T H A N 75% DECI DUOUS .

                                TR E E S  5M TA L L A N D                                                 GR E AT E R T H A N 75% E V E RGR E E N .
 FOR E S T > 75%                PI N E-H E M LOCK                  W H I T E PI N E, H E M LOCK A R E T Y PIC A L C A NOP Y D OM I NA N T S. R E D M A PL E A N D R E D OA K C A N
 E V E RGR E E N )              D OM I NA N T W I T H R E D        BE SU BD OM I- NA N T. OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D GR E AT E R T H A N 75%
                                OA K                               E V E RGR E E N.

                                MON TA N E (>2,0 0 0               A H IGH E L E VAT ION (>2,0 0 0 F E E T) C ON IF E R FOR E S T D OM I NAT E D BY R E D SPRUC E A N D B A L SA M
                                F E E T) SPRUC E-F IR              F IR. H E A R T L E AV E D BIRC H IS A C H A R AC T E R IS T IC TR E E A LONG W I T H Y E L LOW BIRC H, W H I T E
                                D OM I NA N T)                     BIRC H, MOU N TA I N M A PL E, S TR I PE D M A PL E, MOU N TA I NS A SH, A N D OC C A SIONA L LY BL ACK
                                                                   SPRUC E AT U PPE R PAT C H E D GE S. DE NSE BE DS OF SPH AGN U M MOS S C OV E R M UC H OF T H E FOR E S T
                                                                   F LOOR, A N D L IC H E NS H A NG FROM T H E TR E E S.

                                LOW -E L E VAT ION                 A LOW E L E VAT ION (
U PL A N D FOR E S T -         OA K/PI N E                       M I X OF OA K, PI T C H PI N E, R E D PI N E, W H I T E PI N E, OR GR AY BIRC H, DE NSE T O OPE N
MIXED                                                            WOODL A N DS W I T H A LOW SHRU B OR GR A S S L AY E R, OR W I T H SPA R SE C OV E R ON DRY ROCK Y
( TR E E S USUA L LY                                             H I L LT OP S A N D OU T CROP S. OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D L E S S T H A N 75%
> 5 M TA L L A N D                                               DECI DUOUS A N D L E S S T H A N 75 % E V E RGR E E N .
FOR E S T < 75%
                               BIRC H-BE EC H-M A PL E/          NOR T H E R N H A R DWOODS SUC H A S SUGA R M A PL E, Y E L LOW BIRC H, A N D BE EC H A R E
DECI DUOUS OR
                               PI N E-H E M LOCK                 C H A R AC T E R IS T IC, E I T H E R FOR M I NG A DECI DUOUS C A NOP Y OR M I X E D W I T H R E D OA K OR
E V E RGR E E N)
                                                                 H E M LOCK (OR I N SOM E C A SE S W H I T E PI N E). OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D
                                                                 L E S S T H A N 75% DECI DUOUS A N D L E S S T H A N 75% E V E RGR E E N.

                               PI N E-H E M LOCK/                M I X OF W H I T E PI N E, H E M LOCK R E D M A PL E, A N D R E D OA K. OV E R A L L TR E E S GR E AT E R T H A N
                               H A R DWOODS                      5M TA L L A N D L E S S T H A N 75% DECI DUOUS A N D L E S S T H A N 75% E V E RGR E E N.

                               SPRUC E - F IR/H A R DWOODS       FOR E S T S W I T H A M I X OF R E D SPRUC E, B A L SA M F IR, BL ACK A N D W H I T E SPRUC E, Y E L LOW
                                                                 BIRC H, PA PE R BIRC H, BE EC H, A N D R E D OR SUGA R M A PL E. T H E SOI L S A R E USUA L LY ROCK Y,
                                                                 MOS T LY W E L L- T O MODE R AT E LY W E L L DR A I N E D BU T W I T H SOM E SOM EW H AT POOR LY
                                                                 DR A I N E D PAT C H E S AT T H E SLOPE BOT T OMS. OV E R A L L TR E E S GR E AT E R T H A N 5M TA L L A N D
                                                                 L E S S T H A N 75% DECI DUOUS A N D L E S S T H A N 75% E V E RGR E E N.

                               TR E E S 2 0%.

                               C E DA R S WA M P                 WOODE D W E T L A N DS, C H A R AC T E R I Z E D BY C E DA R OR PI T C H PI N E. W E T L A N DS W I T H TR E E S >5M
                                                                 TA L L A N D C A NOP Y C OV E R >2 0%.

W ETL A ND-                    E M E RGE N T M A R SH            FR E SH WAT E R M A R SH E S W I T H MOR E-OR-L E S S PE R M A N E N T WAT E R A N D W I T H NON-PE R SIS T E N T
NON FOR E S T E D              (FR E SH WAT E R)                 V EGE TAT ION. W E T L A N DS W I T HOU T TR E E S OR TR E E S
A P P E N DI X C. BR E E DI NG C ODE S

 C ON F IR M E D
       NY                                    N E S T W I T H YOU NG

       NE                                     N E S T W I T H EG G S
       FS                                  C A R RY I NG F EC A L SAC
       FY                                      F E E DI NG YOU NG
       CF                                      C A R RY I NG FO OD
       FL                               R EC E N T LY E D GE D YOU NG
       ON                                      OC C U PI E D N E S T
       UN                PR E V IOUSLY USE D N E S T (USE W I T H C AU T ION)
       DD                                 DIS TR AC T ION DISPL AY
       NB            N E S T BU I L DI NG (E XC E P T WOODPECK E R S & W R E NS )
       CN                           C A R RY I NG N E S T I NG M AT E R I A L
       PE                   PH YSIOLO GIC A L E V I DE NC E, BRO OD PAT C H
 PROB A BL E
        B               WOODPECK E R / W R E N N E S T BU I L DI NG , C AV I T Y
                                        E XC AVAT ION
        A                                   AGI TAT E D BE H AV IOR
        N                           V ISI T I NG PROB A BL E N E S T SI T E
        C                         C OU R T SH I P DISPL AY , C OPU L AT ION
        T                                  T E R R I T ORY DE F E NSE
        P                              PA IR I N SU I TA BL E H A BI TAT
        M                            M U LT I PL E (7 + ) SI NGI NG BIR DS
       S7                      SI NGI NG BIR DS H E A R D 7 + DAYS A PA R T
 POS SI BL E
        S                                       SI NGI NG BIR DS
        H               OB SE RV E D I N A PPROPR I AT E BR E E DI NG H A BI TAT

16
               Maine Nightjar Monitoring Project - Maine Natural History Observatory
Maine Nightjar and Crepuscular Bird Monitoring Protocol

                                      Survey Route Description Form

Route Name:                                                                              Year:

This form has three purposes:
  • Record specific information on the observer assigned to a specific nightjar route
  • Provide a space where observers can record details about each point location during a non-sur-
      vey visit to the route. These will have been provided to you if the route has been conducted and
      described previously.
  • Allow for recording of habitat information at each stop along a route.

Part 1: Observer Information
                                                                     Observer
                Name
              Address
          City, State, Zip
          Phone Number
          Email Address

Parts 2 and 3: Route Information
  Point                   Location Description                                    # build-   Dominant 3 hab-
                  (visible within 100 meters of point)                            ings       itats
                                                                                  visible    (see below)
     1
     2
     3
     4
     5
     6
     7
     8
     9
     10

         Habitat Codes:
         A. Developed                                 F. Upland Forest - Mixed           K. Open Water
         B. Cultivated Land                           G. Upland Scrub/shrub              L. Alpine/subalpine
         C. Grassland/low herbs                       H. Wetland - Forested
         D. Upland Forest - Deciduous                 I. Wetland - Non-forested
         E. Upland Forest - Evergreen                 J. Bare Land

10
Wind Codes                          Sky Codes                  Noise Codes
                 Maine Sunset Bird Survey Form                                 0 Calm (
12
                                                                               Wind Codes                          Sky Codes                  Noise Codes
               Maine Moonrise Bird Survey Form                                 0 Calm (
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