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B
J
BigCreekR
January1to
BigUnive
Qu
DEMOSUMANUIN
M
The mis
environm
producti
among
Research&E
oMarch31,2
gCreeersityo
uarterl
EMOONITSTAANAUTRIBIG
Mission of
ssion of the D
ment, cultivat
ve citizenship
g the citizens
co
ExtensionTe
2014
ekResofArka
yRepo
NSTTORAINAGEMIENTGCRE
the Unive
Division of Agr
te the improv
p among yout
of the state,
ommunities ac
eam
searchansasSy
ort–Jan
TRATRINGABLEMENTSOEEK
rsity of Ar
riculture is to
vement of ag
th and adults
ensure a safe
cross Arkansa
Dr. Ma
Vice Presid
handystemD
nuary1
TINGGTHENTOONCKWA
kansas Sys
o advance the
riculture and
, enhance eco
e, nutritious f
as, and streng
ark J. Cochr
dent for Agri
dExteDivisio
1toMa
GANE
FC&HATER
stem Divis
e stewardship
agribusiness
onomic secur
food supply, i
gthen Arkans
ran
iculture
Qu
nsiononofAg
arch31
ND
FARRSH
sion of Agr
p of natural re
s, develop lea
rity and finan
improve the q
as families.
uarterlyRep
Page|1
nTeamgricultu
1,2014
RMED
riculture
esources and
dership skills
cial responsib
quality of life
port
mure
the
and
bility
in
B
J
BigCreekR
January1to
DEMOSUSTAFARM
Execut
This
progress m
1. Perm
the la
in sur
comp
below
storm
2. An ag
Big Cr
3. An ag
holdin
4. Flow
subwa
Memo
obtain
5. Field
surfac
mg/kg
6. Base f
from
at the
down
MPN/
7. A seco
furthe
from
applic
8. Work
instal
evapo
inform
Research&E
oMarch31,2
ONSTRAAINABLMINBIG
tiveSumm
is the second
made from Ja
ission was ob
ndowners of
rface runoff a
pleted and Fie
w the C&H Far
m flow sample
greement was
reek gauging
greement was
ng ponds. Da
monitoring e
atershed that
orandums of
ned from Cou
12 was grid s
ce 0 to 4 inch
g.
flow sampling
a spring belo
e spring, 0.007
nstream of the
/100 mL upst
ond set of ma
er document
the first pond
cation of nutr
has begun o
led to measu
oration inform
mation, will b
ExtensionTe
2014
ATINGALEMANGCREEK
mary
d Quarterly Re
anuary 1 thro
btained and si
Fields 1 and
nd water infi
eld 12 is ongo
rm to install f
ers to monitor
s obtained to
stations.
s also reached
ata will be ava
quipment an
t contains the
Understandi
unty Judge to
ampled in the
soil test P co
g of Big Creek
w monitored
7 to 0.014 mg
e Farm. E. co
ream of C&H
anure sample
the naturally
d to the secon
rients to more
n quantifying
re barn wash
mation was al
e used in nut
eam
ANDMONAGEMEKWATE
eport of the B
ugh March 3
igned Memor
12, to install
ltrating throu
ing. Permissi
flow gauging
r nutrient and
cooperate w
d with C&H to
ailable in the
d autosample
e C&H livesto
ng (MOU) an
install this eq
e same mann
oncentrations
k continued e
Field 1. Diss
g/L in Big Cre
oli ranged from
, and 5 to 262
es from Pond
y occurring ma
nd. The resul
e closely mat
g manure volu
h water added
lso obtained.
trient applicat
ONITORENTOFERSHED
Big Creek Rese
1, 2014.
randums of U
flumes and p
ugh the soil pr
ion and signe
stations that
d suspended
with U.S. Geolo
o sample a gr
next quarter.
ers were insta
ck operation
d permission
quipment on
ner as Fields 1
s ranged from
every two wee
solved P conc
ek above the
m <1 to 248 M
20 MPN/100
1 and a first s
anure solids a
lting differenc
ch forage nut
ume and nutr
d to the manu
This informa
tion and solid
RINGTHFNUTRID
earch and Ext
Understanding
piezometers t
rofile. Instru
ed MOUs wer
will be instru
sediment con
ogical Survey
roundwater w
.
alled on the c
and holding
to install and
the County‐o
1 and 5, with
m 17 to 147 m
eks above an
entration ran
e C&H Farm, a
MPN/ 100 mL
mL downstre
set from Pond
and nutrient
ce in manure
trient needs.
rient producti
ure. Historica
ation, in conju
ds separation
Qu
HEIENTSO
tension Team
gs (MOUs) we
to monitor flo
mentation of
re obtained fo
umented with
ncentrations.
y to calibrate a
well adjacent
culvert drainin
ponds. A sign
d access samp
owned culver
40 profiles co
mg P/kg, with a
d below the C
nged from 0.0
and 0.007 to 0
L in spring wa
eam of C&H.
d 2 were colle
stratification
e composition
ion. Water m
al monthly pr
unction with
calculations.
uarterlyRep
Page|2
ONC&H
m that details
ere obtained
ow and nutrie
f Field 1 was
or land above
h continuous
and operate t
to the slurry
ng the
ned
pling stations
rt.
ollected. The
an average of
C&H Farm, an
006 to 0.010 m
0.015 mg/L
ater, 6 to 248
ected, which
with depth a
n, may allow
meters were
recipitation an
animal popu
.
port
H
with
ents
e and
and
the
s was
e
f 63
nd
mg/L
and
nd
lation
B
J
BigCreekR
January1to
BigCre
Faculty
Andrew S
phosphor
Kris Brye,
effects of
related to
Rick Cartw
Resources
Mark Coc
Mike Dan
Brian Hag
quality ch
in aquatic
Jun Zhu, P
treatment
Nathan M
Mary Sav
ecosystem
Karl VanD
mortality
Thad Scot
bodies
Adam Wi
FieldTe
The Big Cr
Technicia
Research&E
oMarch31,2
eekResea
y
Sharpley, Ph.D
rus chemistry
, Ph.D., Profe
land use and
o soil quality a
wright, Ph.D.
s
chran, Ph.D., –
niels, Ph.D., P
ggard, Ph.D.,
hemistry, wat
c systems
PhD., Profess
t technologie
McKinney, Ph.
in, Ph.D. ‐ Str
ms, microorga
Devender, Ph
management
tt, Ph.D., Asso
llis, M.Sc., Ne
echnicians
reek Research
ns based in L
ExtensionTe
2014
archTeam
D., TEAM LEA
, agricultural
ssor ‐ Effects
d managemen
and sustainab
, Professor –
– Vice Preside
rofessor – Ex
Professor ‐ Ec
er quality mo
or ‐ Biologica
es
.D., – Assistan
ructure and f
anisms in nut
.D. and P.E.,t, nutrient ma
ociate Profes
ewton County
s
h and Extensi
ittle Rock and
eam
m
ADER – Distin
management
of land appli
nt practices o
bility
Associate Dir
ent, Universit
xtension wate
cological eng
onitoring and
al and agricult
nt Director, A
unction of mi
rient cycling,
, Professor ‐ Eanagement p
sor ‐ Water q
y Extension A
ion Team are
d Fayetteville
guished Profe
t
cation of pou
n soil physica
rector of Exte
ty of Arkansa
er quality and
ineering, env
modeling, alg
tural enginee
Agriculture Ex
icrobial comm
contaminant
Extension Eng
planning
quality, transp
Agent ‐ Agricu
ably support
.
essor ‐ Soil sc
ultry litter on
al, chemical, a
ension for Agr
s System Divi
nutrient man
vironmental s
gal nutrient li
ering, agricult
xperiment Sta
munities in na
t degradation
gineer, Livesto
port of contam
ulture
ted by severa
Qu
cience, water
in‐situ nutrie
and biologica
riculture and
ision of Agric
nagement sp
oil and water
imitation, po
ural sustaina
ation
atural and ma
n
ock and poult
minants to an
l excellent Pr
uarterlyRep
Page|3
quality, soil
ent leaching,
l properties
Natural
ulture.
ecialist
r sciences, wa
llutant transp
bility, manure
anaged
try manure an
nd within wat
rogram
port
ater
port
e
nd
ter
B
J
BigCreekR
January1to
Tableo
Executive
Big Creek
Faculty
Field Te
List of T
List of F
Introduct
Soil Samp
Manure S
Manure
Water Sam
Samplin
Samplin
Future Pla
Manure
Alterna
ListofTTable 1. A
durin
Table 2. C
and M
Table 3. H
Anim
Table 4. W
per 1
Table 5. W
Farm
Table 6. S
Table 7. S
Table 8. S
Research&E
oMarch31,2
ofConten
Summary ....
Research Tea
y ....................
echnicians ....
Tables ..........
Figures .........
ion ...............
pling and Anal
Slurry Samplin
e Production
mpling and A
ng Locations
ng Protocols a
an of Work ...
e Treatment v
ative Manure
TablesAverage soil t
ng the Compr
Chemical pro
March 10, 20
Historical ann
mal Waste Ma
Water quality
100 mL of wat
Water quality
m boundary of
Soil analyses o
Soil analyses o
Soil analyses o
ExtensionTe
2014
nts
.....................
am ................
.....................
.....................
.....................
.....................
.....................
lysis ..............
ng and Analys
Determinatio
nalyses.........
.....................
and Analyses
.....................
via Solids and
Managemen
test P concen
rehensive Nut
perties of ma
14. ...............
nual precipita
anagement So
y analyses at e
ter. ...............
y analyses at t
f permitted la
of 0 to 4 inch
of 4 to 8 inch
of 8 to 12 inc
eam
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
sis ..................
on .................
.....................
.....................
....................
.....................
d Chemical Se
t Options .....
trations in th
trient Manag
anure sample
.....................
tion informat
oftware progr
each sample
.....................
the spring an
and applicatio
samples coll
samples coll
h samples co
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
eparation: A C
......................
e surface 0 to
ement Plan (C
s collected fro
......................
tion for Newt
ram version 2
site. Coliform
......................
d in Big Creek
on fields (see
ected from F
ected from F
ollected from
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
Case Study to
.....................
o 4 inches of
CNMP) devel
om ponds 1 a
.....................
ton Co. Arkan
2.4.0. ............
m units are M
.....................
k upstream a
Map 12). .....
ield 12. ........
ield 12. ........
Field 12. ......
Qu
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
o Evaluate Cos
.....................
each field an
lopment........
and 2 on Sept
.....................
nsas. Extracte
.....................
Most Probable
.....................
nd downstrea
.....................
.....................
.....................
.....................
uarterlyRep
Page|4
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
......................
st Benefits of
......................
d when samp
......................
tember 24th,
......................
ed from NRCS
......................
e Number (MP
......................
am of the C&
......................
......................
......................
......................
port
....... 2
....... 3
....... 3
....... 3
....... 4
....... 5
....... 6
....... 7
..... 12
..... 12
..... 19
..... 19
..... 28
..... 44
f
..... 44
pled
....... 7
2013
..... 16
’s
..... 17
PN)
..... 29
&H
..... 39
..... 46
..... 48
..... 50
B
J
BigCreekR
January1to
Table 9. S
Table 10.
ListofF
Figure 1.
Newt
Figure 2.
Newt
Figure 3.
Newt
Figure 4.
Newt
Figure 5.
........
Figure 6.
Figure 7.
Figure 8.
wate
Figure 9.
wate
and 2
Figure 10
Figure 11
on th
Figure 12
Figure 13
Figure 14
oper
Figure 15
Figure 16
Figure 177
Research&E
oMarch31,2
Soil analyses o
Soil analyses
Figures
Gridded layo
ton County, A
Soil P distribu
ton County, A
Soil P distribu
ton County, A
Soil P distribu
ton County, A
Select Chemi
.....................
Select chemi
Select Chemi
One of the st
er use during
Two water m
er additions to
2. ..................
. Location of
. Topographi
he C&H Farm
. Location of
. Edge‐of‐fiel
. The culvert
ation facilitie
. The spring s
. The Big Cre
7. The Big Cr
ExtensionTe
2014
of 12 to 18 in
s of 18 to 24 i
out of the sam
AR. ................
ution of the 0
AR. ................
ution of the 0
AR.3. .............
ution of the 0
AR. ................
ical propertie
.....................
cal propertie
ical propertie
tandard wate
pressure was
meters purcha
o manure vol
.....................
water quality
c elevation m
. ....................
water quality
ld surface run
sampling an
es. .................
sampled adja
ek sampling s
eek sampling
eam
nch samples c
inch samples
mpled Field 1,
.....................
0 to 4 inch de
.....................
0 to 4 inch de
.....................
0 to 4 inch de
.....................
es of manure
.....................
s of manure s
es of manure
er meters with
shing to clean
ased and insta
ume. Initial m
.....................
y sampling sit
map showing
.....................
y sampling sit
noff flume on
ephemeral st
.....................
cent to Big C
site upstream
g site downstr
collected from
collected fro
5, and 12 on
......................
pth for Field
......................
pth for Field
......................
pth for Field
......................
samples colle
......................
samples colle
samples colle
h hose adapte
n animal pens
alled on Marc
meters readin
......................
tes on Big Cre
low point wh
......................
tes on Big Cre
Field 1 on th
tream drainin
......................
reek on the C
m of the C&H
ream of the C
m Field 12. ....
om Field 12. ..
n the C&H Far
.....................
1 on the C&H
.....................
5 on the C&H
.....................
12 on the C&
.....................
ected from po
.....................
ected from po
ected from po
ers and moun
s. ...................
ch 20th, 2014
ngs were 126.
.....................
eek and sprin
here any surfa
.....................
eek and the C
he C&H Farm.
ng a subwate
.....................
C&H Farm. ....
Farm during
C&H Farm dur
Qu
.....................
.....................
rm operation
.....................
H Farm opera
.....................
H Farm opera
.....................
&H Farm oper
.....................
ond 1 on Sept
.....................
ond 1 on Mar
ond 2 on Mar
nting base ins
.....................
4 to measure
.6 and 80.2 ga
.....................
g below appl
ace runoff wo
.....................
C&H Farm. .....
. ....................
rshed contain
.....................
.....................
baseflow. .....
ring baseflow
uarterlyRep
Page|5
......................
......................
Mt. Judea,
......................
tion Mt. Jude
......................
tion Mt. Jude
......................
ration Mt. Jud
......................
tember 24, 2
......................
rch 10, 2014. .
rch 10, 2014. .
stalled to mea
......................
pen wash do
allons for met
......................
ication Field
ould leave Fie
......................
......................
......................
ning the C&H
......................
......................
......................
w. ...................
port
..... 52
..... 54
....... 8
ea,
....... 9
ea,
..... 10
dea,
..... 11
013.
..... 13
..... 14
..... 15
asure
..... 18
own
ter 1
..... 18
1. . 20
ld 12
..... 21
..... 22
..... 23
Farm
..... 24
..... 25
..... 26
..... 27
B
J
BigCreekR
January1to
Introdu
This
operation
fields) on
1. Monit
applie
2. Asses
the w
stream
3. Deter
includ
water
The p
of current
with nutri
added wit
and envir
treatment
which has
export of
The p
investigat
pass flow
This
will not co
waters. A
minimum
Natural R
required t
Research&E
oMarch31,2
uction
research proj
n (subsequent
the water qu
tor the fate a
ed swine efflu
s the impact
water quality o
ms.
rmine the effe
ding solid sep
rshed.
project will m
t manure man
ient levels in
th landowner
onmental sus
t, which is reg
s the potentia
treated man
plan of resear
tion, such as t
pathways co
information w
over long‐term
Additional fun
of five years
esources Con
to accurately
ExtensionTe
2014
ject will evalu
tly referred to
uality of Big C
nd transport
uent to pastu
of farming op
of Big Creek b
ectiveness an
aration, whic
measure soil fe
nagement on
surface runof
r permission),
stainability co
garded as add
al to provide t
ures off the f
rch meets the
the use of dye
mmon in kar
will be a shor
m monitoring
nds would be
. This time fr
nservation Se
assess any im
eam
uate the impa
o as C&H, to i
reek. The stu
of nitrogen (
res.
perations (eff
below the C&
nd sustainabil
ch may enhan
ertility levels
n nutrient bala
ff and monito
, will guide ad
oncerns. The
dressing nutr
the farm with
arm and/or o
e level of fund
e‐tracer tests
st dominated
t‐term assess
g, sample ana
needed for s
rame is recog
rvice (NRCS),
mpacts and ov
act and sustai
include anima
udy includes t
N), phosphor
fluent holding
H Farm as we
ity of alterna
nce transport
of all permitt
ances (i.e., an
ored wells on
daptive manu
project will a
ient imbalanc
h cost‐benefic
out of the wat
ding currently
s, will provide
d areas will be
sment and it m
alysis, and ass
ample collect
nized by the
and general
vercome ann
inable manag
al facilities an
the following
rus (P), sedim
g ponds and l
ell as emergin
tive manure
and export o
ted fields ann
ny potential a
Fields 1 and
ure managem
also assess th
ce concerns o
cial alternativ
tershed.
y available. O
e valuable info
e conducted.
must be note
sessment of la
tion and labo
Environment
scientific com
ual weather f
Qu
gement of the
nd permitted
g major tasks:
ment, and bac
and‐applicati
ng springs and
management
of nutrients o
nually, to dete
accumulation
12 (an additi
ment decisions
e feasibility o
on all farms s
ve for the sus
Other importa
ormation on
ed that funds
and use impa
or to continue
tal Protection
mmunity to be
fluctuations.
uarterlyRep
Page|6
e C&H Farm
land applicat
teria from lan
ion of effluen
d ephemeral
t techniques,
ut of the
ermine the im
). This comb
onal Field wi
s to address f
of manure
imilar to C&H
tainable use
ant methods
possible rapid
allocated bel
acts on area
e monitoring f
n Agency (EPA
e the minimu
port
tion
nd‐
nt) on
mpact
ined
ll be
field
H,
and
of
d by‐
low
for a
A),
um
B
J
BigCreekR
January1to
SoilSam
Grid
acres and
to 24”, 24
on each fi
after the s
rock stopp
The a
and avera
quarter of
are given
Tablesa
† NS
Research&E
oMarch31,2
mplingan
soil sampling
seven soil‐de
4 to 30”, and 3
ield to determ
soil core was
ped the core
actual analyse
ages in Table
f this project.
in Figures 2,
e 1. Average ampled durin
S is Not Samp
ExtensionTe
2014
ndAnalys
g of Field 12 w
epths increm
30 to 36” whe
mine the poin
removed wa
penetrating b
es of each co
1. Table 1 co
. The distribu
3, and 4, resp
soil test P cong the Compr
Soil depth,
Original N
0 ‐ 4
4 – 8
8 – 12
12 – 1
18 – 2
24 – 3
led.
eam
sis
was conducte
ents were co
ere possible w
nt of sampling
s carefully ba
below a speci
re sample an
ontains averag
ution of soil te
pectively.
oncentrationsrehensive Nu
inches
NMP
8
2
18
24
30
d as per Figur
llected to inc
with a Giddin
g, which was
ack‐filled with
ific layer, no s
d depth are g
ge values for
est P in the su
s in the surfautrient Manag
Field 1
‐ ‐ ‐ ‐ ‐ ‐ ‐
83
41
17
10
NS †
NS
NS
re 1. The grid
clude 0 to 4”,
ngs soil probe
noted by GPS
h commercial
sample was t
given in Appe
Fields 1 and 5
urface 4 inche
ce 0 to 4 inchgement Plan
Field 5
‐ ‐ ‐ mg/kg ‐
65
54
32
28
34
6
19
Qu
d size is appro
4 to 8”, 8 to
. A grid netw
S. Each samp
top soil (see
taken.
endix (Table 6
5 already com
es of soil of F
hes of each fi(CNMP) deve
Field 12
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
19
63
36
26
24
35
NS
uarterlyRep
Page|7
oximately 0.2
12”, 12 to 18
work was over
ple‐hole rema
Figure 1). W
6, 7, 8, 9, and
mpleted in th
ields 1, 5, and
eld and whenelopment.
port
25
”, 18
rlain
ining
Where
10)
e first
d 12
n
Big
Janu
CreekResearch
uary1toMarch
Figur
h&ExtensionT
h31,2014
re 1. Gridded lay
Team
yout of the samp
pled Field 1, 5, an
nd 12 on the C&H
H Farm operation
n Mt. Judea, New
Quarte
wton County, AR.
erlyReport
Page|8
BQ
J
BigCreekRQuarterlyRe
January1to
Figure 2.
Research&Eeport
oMarch31,2
Soil P distrib
ExtensionTe
2014
bution of the
eam
e 0 to 4 inch dNewto
depth for Fielon County, A
ld 1 on the C&AR.
&H Farm ope
Page|
eration Mt. Ju
9
udea,
BQ
J
BigCreekRQuarterlyRe
January1to
Figure 3.
Research&Eeport
oMarch31,2
Soil P distrib
ExtensionTe
2014
bution of the
eam
e 0 to 4 inch dNewto
depth for Fieln County, AR
ld 5 on the C&R.3.
&H Farm ope
Page|
eration Mt. Ju
10
udea,
BQ
J
BigCreekRQuarterlyRe
January1to
Figure 4.
Research&Eeport
oMarch31,2
Soil P distrib
ExtensionTe
2014
bution of the
eam
0 to 4 inch deNewto
epth for Fieldon County, A
d 12 on the CAR.
C&H Farm ope
Page|
eration Mt. J
11
udea,
B
J
BigCreekR
January1to
Manur
To pr
set of ma
point that
Ponds 1 a
As w
samples r
settled so
the pond
subsampl
sample re
hand‐deli
Figures 5,
As w
samples f
chemical
concentra
How
higher N /
the C&H F
both the N
concentra
banking a
C&H Farm
Even
natural gr
opportun
nutrient c
that it ret
differentia
ManureThe v
populatio
down wat
increase m
feeders so
feed. As a
Research&E
oMarch31,2
reSlurryS
rovide additio
nure samples
t it flowed ac
nd 2
ith the first sa
representing m
olids at the bo
including the
es from vario
epresenting th
vered on the
6, and 7)
ith the Septe
rom Ponds 1
profiles typic
ations of the m
ever, P conce
/ P ratio of th
Farm. Thus, l
N and P need
ation and low
pproach, whe
m and Big Cree
without the
ravity separat
ities to more
concentration
ains a signific
al manure ma
eProductivolume of ma
on characteris
ter. In additio
manure volum
o that any an
a result there
ExtensionTe
2014
Sampling
onal informat
s were collect
ross the spill
ampling even
manure from
ottom of the p
e settled solid
ous locations
he top water,
day of collec
mber 24, 201
and 2, repres
al of other m
manure incre
entrations inc
e surface wat
and applicati
s of the pastu
wer N / P ratio
ere the slurry
ek.
addition of m
tion of slurry
closely matc
ns of Pond 1 o
cant portion o
anagement o
ionDetermanure produc
stics, freshwa
on, any precip
me. Discussio
imal drinking
will be effect
eam
andAnal
tion for the ad
ted on March
way into Pon
nt, a foot valv
6 inches belo
pond (bottom
s (pond profi
around the p
, pond profile
ction to the U
13 samples th
senting the to
anure storag
eased with wa
creased at a g
ter is closer t
on of top wat
ure and avoid
o of bottom sl
y would be ap
mechanical an
and its const
h manure nut
over Pond 2 c
of the manure
pportunities
minationed by livestoc
ter additions
pitation direc
ons with C&H
water spillag
tively no spille
lysis
daptive manu
h 10, 2014. Th
nd 2. Thus, the
ve liquid manu
ow the water
m slurry), and
le). Each com
pond. These s
e, and bottom
ofA Agricultu
he March 10,
op water, bot
es associated
ater depth (Fi
greater rate th
o the ratio of
ter from a po
d application
lurries will len
pplied on alte
nd/or chemica
ituents, provi
trients to cro
onfirm that P
e solids and n
pertaining to
ck is largely d
(if any), spille
ctly into manu
managemen
ge would fall
ed drinking w
ure managem
he water leve
e March 10, 2
ure sampler w
r surface (top
from the wa
mposite samp
subsamples w
m slurry of Pon
ural Diagnosti
2014 collecti
ttom slurry, a
d with swine p
igures 6 and 7
han did N con
f these nutrie
ond to farm p
of P surplus t
nd to applicat
ernate years t
al separation
ides farm nut
op nutrient ne
Pond 1 is func
nutrients. Th
o land applica
determined b
ed drinking w
ure storage o
nt revealed th
into feed trou
water adding t
Qu
ment decision
el in Pond 1 h
2014 samples
was used to c
p water), from
ter surface to
ple was comp
were mixed to
nds 1 and 2 o
ics Service La
on and analy
and entire pro
production. T
7).
ncentrations.
ents required
astures will m
to plant need
tion of that sl
to fields more
approaches,
trient manage
eeds. In addit
ctioning as se
is provides ad
tion.
y the average
water (if any),
or via surface
hat the farm u
ughs to be co
to manure vo
uarterlyRep
Page
process a se
ad reached th
s were drawn
collect compo
m within the
o the bottom
posed of mult
o compose a
obtained and
boratory (Tab
ysis of manure
ofile, generate
That is, N and
The resultin
by pastures o
more likely m
s. The highe
lurry on a ma
e distant from
the observed
ement
tion, the high
ettling basin, i
dditional
e animal
and pen was
runoff will
used “wet/dry
onsumed with
olume.
port
|12
cond
he
n from
osite
of
iple
ble 2
e
ed
d P
g
on
eet
r
anure
m the
d
her
in
sh‐
y”
h the
B
J
BigCreekR
January1to
Estim
the flow r
determina
were purc
(Figure 8 a
Futu
amount o
quantify p
the built d
informatio
additions
Figure
K AS "
N/P
P AS "P2
% S
Research&E
oMarch31,2
mates for pen
rates in gallon
ation of pen‐w
chased and in
and 9).
re meter read
of water used
potential prec
dimensions a
on (Table 3) w
to the manu
5. Select Che
0.6
1.35
2.9
1.25
1.15
2.5
2.4
0.74
2.5
0.63
0
"K20"
P2O5
WEP
2O5"
N
Solids
ExtensionTe
2014
‐wash down
ns per minute
wash water a
nstalled to me
dings and the
on a daily ba
cipitation add
nd elevations
will be include
re volume.
emical prope
11.58
5
13.04
99
10.54
5
5
10.06
12.61
56
10.8
47
57
6.36
10 2
lb/1
eam
water were p
e, and the ave
additions to th
easure all the
e date of the r
asis to wash th
ditions to the
s of Ponds 1 a
ed in the info
erties of man
21.73
0 30
000 gallons, R
Pond 1, Se
provided in th
erage time sp
he manure w
e water used b
readings will
he animal pe
manure volu
and 2. This in
ormation used
ure samples 2013.
40
Ration Values U
eptember 24
he form of the
pent washing
was desired, tw
by two pressu
provide meas
ns and added
ume planning
nformation an
d to estimate
collected fro
50 60
Unitless, On W
4, 2013
Qu
e number of p
each day. As
wo standard w
ure washers u
sured inform
d to the manu
is in progress
nd historical r
e potential pre
m pond 1 on
0 70
Wet As‐Is‐Basis
To
Pr
Bo
uarterlyRep
Page
pressure was
s a more direc
water meters
used in the ba
ation on the
ure volume. T
s to determin
rainfall
ecipitation
September 2
80
op
rofile
ottom
port
|13
shers,
ct
s
arns
To
ne as
24,
90
B
J
BigCreekR
January1to
Figure 6
K AS "
N/P
P AS "P2
% S
Research&E
oMarch31,2
6. Select che
0.53
4
1.24
1.62
3
4
0.77
3.
0.95
0
"K20"
P2O5
WEP
2O5"
N
Solids
ExtensionTe
2014
emical proper
16
4.86
13.84
14.3
4
2
1
.62
13.70
4.10
.40
13.94
5
10 2
lb/1
eam
rties of manu
.06
4
6
18.10
22.40
0
4
0 30
000 gallons, R
Pond 1,
ure samples c
43
40
Ration Values U
March 10, 2
collected from
3.77
50 60
Unitless, On W
2014
Qu
m pond 1 on M
0 70
Wet As‐Is‐Basis
uarterlyRep
Page
March 10, 20
82.7
80
Top
Profile
Bottom
port
|14
014.
77
90
B
J
BigCreekR
January1to
Figure 7
K AS "
N/P
P AS "P2
% S
Research&E
oMarch31,2
7. Select Che
1.90
1.13
3.
3.
0.66
3.0
0.98
4
0.64
2.3
0.62
0
K20"
P2O5
WEP
2O5"
N
Solids
ExtensionTe
2014
emical proper
12.31
0
7.74
14.7
.71
12.26
.81
05
11.63
12.14
4.34
37
10.29
10 20
lb/10
eam
rties of manu
74
0 30
000 gallons, Ra
Pond 2,
ure samples c
40
ation Values U
March 10, 2
collected from
50 60
Unitless, On W
2014
Qu
m pond 2 on
0 70
Wet As‐Is‐Basis
uarterlyRep
Page
March 10, 20
80
Top
Profile
Bottom
port
|15
014.
90
Big
Janu
pH
Elect(umh
Solid
Total
NH4‐
NO3‐
Total
WEP
Total
Total
NH4‐
WEP
N / P
N:P2O
†
CreekResearch
uary1toMarch
Table 2.
trical conductivityhos/cm)
s (%)
l N (lbs/1000 gal)
N (lbs/1000 gal)
N (lbs/1000 gal)
l P as "P2O5" (lbs/
(lbs/1000 gal)
l K as "K20" (lbs/1
l Ca (lbs/1000 ga
N / Total N
/ Total P
P2O5
O5:K2O ratio
† "<" indicate the
h&ExtensionT
h31,2014
Chemical prope
0
y 1
)
<0
/1000 gal)
1000 gal) 1
l)
2
e NO3‐N value is b
Team
erties of manure s
September 2
Pond
0 – 6” Prof
7.8 7.7
10020 100
0.63 2.5
6.36 12.6
6.09 7.2
0.006 † <0.0
2.57 10.0
0.74 1.1
10.80 10.5
0.29 3.1
0.96 0.5
0.66 0.2
2.47 1.2
2:1:4 1:1
below detection l
samples collecte
24th, 2013
d 1
file Bottom
7 7.6
060 9880
56 2.99
61 13.04
29 6.31
006 <0.006
06 21.73
15 1.35
54 11.58
16 7.71
58 0.48
26 0.14
25 0.60
:1 1:2:1
imits.
ed from ponds 1 a
S
0 – 6”
7.8
14830
0.95
13.94
12.45
<0.001
3.40
0.77
13.70
1.26
0.89
0.52
4.10
4:1:4
and 2 on Septem
Sample Date
Pond 1
Profile
7.5
14770
3.62
22.40
13.14
<0.001
18.10
1.62
14.36
7.66
0.59
0.20
1.24
2:1:1
mber 24th, 2013 a
March 10th, 20
Bottom 0 –
7.3 8
10860 12
13.84 0
43.77 10
13.44 9
<0.001 0.
82.77 2
4.86 0
16.06 12
41.65 0
0.31 0
0.13 0
0.53 4
3:5:1 4:
Quarte
and March 10, 20
014
Pond
– 6” Profile
8.0 7.9
2640 12490
.62 0.98
0.29 11.63
.79 10.42
002 <0.001
.37 3.05
.64 0.66
2.14 12.26
.66 1.15
.95 0.90
.62 0.50
4.34 3.81
:1:5 4:1:4
rlyReport
Page|16
014.
2
e Bottom
7.8
0 12370
3.71
3 14.74
2 10.28
1 <0.001
7.74
1.13
6 12.31
3.87
0.70
0.33
1.90
2:1:2
B
J
BigCreekR
January1to
Table 3.
Research&E
oMarch31,2
Historical anA
ExtensionTe
2014
nnual precipitAnimal Waste
Mo
Janu
Febr
Ma
Ap
M
Ju
Ju
Aug
Septe
Octo
Nove
Dece
Tot
eam
tation informe Managemen
onth Pre
uary
ruary
arch
pril
ay
ne
uly
gust
ember
ober
ember
ember
tals
mation for Nent Software p
ecipitation
2.06
2.75
4.58
3.97
5.06
3.27
2.94
2.74
4.15
3.47
3.88
3.55
42.42
wton Co. Arkprogram vers
Evaporatio
0.72
1.08
2.52
3.60
4.68
4.68
5.40
5.04
3.24
2.88
1.44
0.72
36.00
Qu
kansas. Extrasion 2.4.0.
on
uarterlyRep
Page|
cted from NR
port
17
RCS’s
B
J
BigCreekR
January1to
Figure
Figure 9. water a
Research&E
oMarch31,2
e 8. One of thmea
Two water madditions to m
ExtensionTe
2014
he standard wasure water u
meters purchmanure volum
eam
water metersuse during pr
hased and insme. Initial me
s with hose aressure wash
talled on Maeters readingsand 2.
adapters and ing to clean a
arch 20th, 201s were 126.6
Qu
mounting baanimal pens.
14 to measur6 and 80.2 gal
uarterlyRep
Page|
ase installed t
re pen wash dllons for met
port
18
to
down er 1
B
J
BigCreekR
January1to
Water
Samplin
Topo
location f
where the
construct
of the far
Wate
(Figure 12
runoff mo
13. Addit
stream dr
are locate
Site 1.
Site 2.
Site 3.
Site 4.
Site 5.
Site 6.
Site 7.
Research&E
oMarch31,2
Sampling
ngLocatio
ographic surve
or edge‐of‐fie
e flume was s
ion will begin
med field.
er quality sam
2). Since Janu
onitoring equ
tionally runof
raining a sub‐
ed, as shown
Edge‐of fie
Edge‐of fie
Edge‐of fie
Ephemera
14.
Spring belo
Big Creek u
Big Creak d
ExtensionTe
2014
gandAna
ons
eys of permit
eld surface ru
sited. The loc
n as soon as th
mpling was ini
uary 1 and rep
ipment was c
f volume and
watershed in
in Figure 12.
eld monitorin
eld monitorin
eld monitorin
l stream flow
ow Field 1 – F
upstream of t
downstream
eam
alyses
tted Fields 1 a
unoff collectio
cation for a si
he Field dries
itiated on Sep
ported in the
completed an
d auto‐sampli
n which the C&
These sites a
g on Field 1 p
g on Field 5a
g on Field 12
w draining a su
Figure 15.
the C&H Farm
of the C&H F
and 12 were c
on flumes. Fig
milar flume o
s to allow con
ptember 24, 2
1st Quarterly
nd became op
ng equipmen
&H Farm ope
are;
permitted to
– still to be d
permitted to
ubwatershed
m operation –
arm operatio
conducted to
gure 10 show
on Field 12 is
nstruction wit
2013, prior to
y Report, insta
perational Ap
nt was also ins
erations and s
receive slurry
determined
o receive slur
containing th
– Figure 16.
on – Figure 17
Qu
o determine th
ws the low po
shown on Fig
thout damagi
o the formal s
allation of ed
ril 2, 2014, as
stalled on an
swine slurry s
y – Figure 13.
ry – still to be
he production
7.
uarterlyRep
Page|
he appropriat
int on Field 1
gure 11 and
ng or rutting
start of the pr
ge‐of‐field su
s shown in Fig
ephemeral
storage lagoo
e completed
n facilities – F
port
19
te
1
any
roject
urface
gure
ns
Figure
B
J
BigCreekR
January1to
Figure 10
Research&E
oMarch31,2
0. Location o
ExtensionTe
2014
of water quali
eam
ity sampling
sites on Big C
Creek and spr
Qu
ring below ap
uarterlyRep
Page|
pplication Fie
port
20
eld 1.
B
J
BigCreekR
January1to
Figure 11
Research&E
oMarch31,2
1. Topograph
ExtensionTe
2014
hic elevation
eam
map showing12 on
g low point wthe C&H Farm
where any sum.
Qu
rface runoff w
uarterlyRep
Page|
would leave
port
21
Field
B
J
BigCreekR
January1to
Research&E
oMarch31,2
Figure 12. Lo
ExtensionTe
2014
ocation of wa
eam
ater quality s
sampling sites
s on Big Cree
Qu
ek and the C&
uarterlyRep
Page|
&H Farm.
port
22
B
J
BigCreekR
January1to
Research&E
oMarch31,2
Figure 1
ExtensionTe
2014
13. Edge‐of‐f
eam
field surface r
runoff flume
on Field 1 on
Qu
n the C&H Fa
uarterlyRep
Page|
rm.
port
23
B
J
BigCreekR
January1to
Figure 1
Research&E
oMarch31,2
14. The culve
ExtensionTe
2014
ert sampling a
eam
an ephemeraFarm op
al stream draieration facili
ining a subwities.
Qu
atershed con
uarterlyRep
Page|
ntaining the C
port
24
C&H
B
J
BigCreekR
January1to
Research&E
oMarch31,2
Figure
ExtensionTe
2014
e 15. The spr
eam
ing sampled
adjacent to B
Big Creek on t
Qu
the C&H Farm
uarterlyRep
Page|
m.
port
25
B
J
BigCreekR
January1to
Research&E
oMarch31,2
Figure 16. T
ExtensionTe
2014
The Big Creek
eam
sampling sit
e upstream o
of the C&H Fa
Qu
arm during ba
uarterlyRep
Page|
aseflow.
port
26
B
J
BigCreekR
January1to
Fi
Research&E
oMarch31,2
gure 177. Th
ExtensionTe
2014
he Big Creek s
eam
sampling site
e downstream
m of the C&H
Qu
Farm during
uarterlyRep
Page|
g baseflow.
port
27
B
J
BigCreekR
January1to
Samplin
The c
4. The fo
1. O
2. W
w
3. T
4. S
5. T
6. S
t
a
7. A
A
S
Research&E
oMarch31,2
ngProtoco
chemical com
llowing proce
One‐liter acid
Water was co
well‐mixed.
The bottle wa
Sterilized spe
Time of collec
Samples were
to the Arkans
analyses.
Analyses inclu
Ammonia (EP
Solids (EPA 16
ExtensionTe
2014
olsandAn
mposition of w
edure was use
d‐washed bot
ollected from
as rinsed with
ecimen cups w
ction was not
e placed in a c
sas Water Res
uded Dissolve
PA 351.2), Nit
60.2), E. Coli (
eam
nalyses
water samples
ed to collect,
tles were use
just beneath
h stream wate
were used to
ted.
cooler on ice
sources Cente
ed Phosphoru
rate (EPA 300
(APHA 9223,
s collected pr
prepare and
ed to collect t
the surface w
er before coll
collect sampl
to preserve t
er Water Qua
us (EPA 365.2
0.0), Total Nit
B) and Total C
rior to Decem
analyze all w
the stream sa
where the str
ecting the sa
les for bacter
them until pr
ality Lab on th
), Total Phosp
trogen (APHA
Coliforms (AP
Qu
mber 31, 2013
water samples
amples for nu
ream was act
mple.
rial evaluation
ocessed and
he day of colle
phorus (APHA
A 4500‐P), Tot
PHA 9223, B).
uarterlyRep
Page|
3 is given in Ta
s;
trient analyse
ively moving
n.
were submitt
ection for
A 4500‐P),
tal Suspended
.
port
28
able
es.
and
ted
d
B
Ja
D
sco
9/
9/
9/
BigCreekResea
anuary1toMar
Table 4.
Date & time
sample ollected
Daterecelab
/12/2013 9/1
10:45 1
11:15 1
11:50 1
13:00 1
/20/2013 9/2
10:50 1
11:15 1
11:40 1
12:20 1
12:50 1
/24/2013 9/2
arch&Extensio
rch31,2014
. Water quality a
e & time eived @ oratory
Saloc
12/2013
15:30 Ups
f
15:30 Ups
b
15:30 Dow
b
15:30 Dow
f
20/2013
16:08 Sp
16:08 Ups
f
16:08 Ups
b
16:08 Dow
b
16:08 Dow
f
24/2013
onTeam
analyses at each
mple cation
DissoP
Base flow
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
sample site. Col
olved P
Total P
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
016 0.030
010 0.032
019 0.026
010 0.022
006 0.020
009 0.022
015 0.024
024 0.032
013 0.022
liform units are M
P Ammonia‐
N
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
0.06
0.05
0.05
0.04
0.03
0.03
0.04
0.06
0.05
Most Probable N
Nitrate‐N T
mg/L ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.367
0.356
0.632
0.396
0.384
0.247
0.356
0.757
0.442
Number (MPN) pe
Total N Tot
suspesoli
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.50 3.
0.54 5.
0.78 1.
0.62 1.
0.50 4.
0.36 1.
0.42 1.
0.85 1.
0.53 1.
Quarter
er 100 mL of wat
tal nded ids
E. coli
‐ ‐ ‐ MP
0 6.3
8 4.1
2 1.0
7 16.0
7 72.7
1 80.9
2 1203
3 218.7
1 548
rlyReport
Page|29
ter.
Total coliform
PN/100 mL ‐ ‐ ‐
>2420
4040.0
488.4
>2420
5040
9870
26130
2430
17230
B
Ja
D
sco
10
10
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
10:30 1
10:45 1
11:00 1
12:20 1
12:40 1
0/1/2013 10/
9:45 1
10:00 1
10:15 1
10:35 1
10:55 1
0/9/2013 10/
9:00 1
9:30 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
16:15 Sp
16:15 Ups
f
16:15 Ups
b
16:15 Dow
b
16:15 Dow
f
/1/2013
14:42 Sp
14:42 Ups
f
14:42 Ups
b
14:42 Dow
b
14:42 Dow
f
/9/2013
13:52 Sp
13:52 Ups
f
onTeam
mple cation
DissoP
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
olved P
Total P
004 0.024
011 0.014
007 0.024
017 0.032
007 0.028
001 0.162
011 0.038
006 0.032
018 0.032
009 0.034
011 0.054
016 0.034
P Ammonia‐
N
0.00
0.03
0.00
1.77
0.01
0.00
0.02
0.03
0.00
0.02
0.00
0.00
Nitrate‐N T
0.122
0.444
0.330
0.790
0.511
0.108
0.236
0.235
0.837
0.514
0.088
0.497
Total N Tot
suspesoli
0.35 50
2.20 17
0.41 1.
0.82 0.
0.58 1.
0.41 89
0.34 2.
0.40 6.
0.92 1.
0.65 3.
0.28 29
0.73 7.
Quarter
tal nded ids
E. coli
.0 8.5
.9 39
6 42
7 42
5 5
.2 4
2 8
7 82
1 19
6 2620
.1 3
1 11
rlyReport
Page|30
Total coliform
>2420
1120
>2419
816
>2420
920
1300
5200
649
10810
1413
2419
B
Ja
D
sco
10/
10/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
9:45 1
10:00 1
10:20 1
/15/2013 10/
11:13 1
12:24 1
12:47 1
13:13 1
13:34 1
/22/2013 10/
10:10 1
10:30 1
10:45 1
11:00 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
13:52 Ups
b
13:52 Dow
b
13:52 Dow
f
/15/2013
15:47 Sp
15:47 Ups
f
15:47 Ups
b
15:47 Dow
b
15:47 Dow
f
/22/2013
15:31 Sp
15:31 Ups
f
15:31 Ups
b
15:31 Dow
onTeam
mple cation
DissoP
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Storm flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream 0.0
olved P
Total P
016 0.030
017 0.02
006 0.038
010 0.250
018 0.026
019 0.036
033 0.244
067 0.316
005 0.086
014 0.034
016 0.024
016 0.022
P Ammonia‐
N
0.00
0.00
0.00
0.15
0.00
0.06
0.12
0.20
0.10
0.00
0.03
0.00
Nitrate‐N T
0.385
0.868
0.618
0.086
1.024
0.839
1.280
0.677
0.307
0.345
0.575
0.786
Total N Tot
suspesoli
0.53 6.
0.89 0.
0.77 13
0.58 66
1.03 1.
0.99 2.
1.44 89
1.07 101
0.53 36
0.32 0.
0.60 1.
0.77 0.
Quarter
tal nded ids
E. coli
2 194
4 29
.6 28
.9 1401
1 759
1 472
.2 959
1.1 1334
.4 1733
3 186
2 411
1 150
rlyReport
Page|31
Total coliform
4730
1986
3450
19863
>2419
8664
12997
19863
>2419
299
11190
2419
B
Ja
D
sco
10/
11
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
11:20 1
/31/2013 10/
11:00 1
10:45 1
10:15 1
10:00 1
10:30 1
1/6/2013 11/
8:35 1
9:00 1
9:10 1
9:45 1
10:00 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
b
15:31 Dow
f
/31/2013
15:15 Sp
15:15 Ups
f
15:15 Ups
b
15:15 Dow
b
15:15 Dow
f
/6/2013
14:35 Sp
14:35 Ups
f
14:35 Ups
b
14:35 Dow
b
14:35 Dow
f
onTeam
mple cation
DissoP
barn
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
olved P
Total P
012 0.020
003 0.404
012 0.032
007 0.044
018 0.022
012 0.024
013 0.130
032 0.074
020 0.038
040 0.164
041 0.154
P Ammonia‐
N
0.04
0.14
0.00
0.04
0.11
0.03
0.10
0.03
0.00
0.12
0.12
Nitrate‐N T
0.723
0.321
0.242
0.246
0.519
0.443
0.062
0.432
0.184
0.413
0.286
Total N Tot
suspesoli
0.76 0.
1.02 400
0.32 1.
0.38 2.
0.66 0.
0.45 1.
0.72 21
0.61 4.
0.27 2.
0.67 32
0.60 28
Quarter
tal nded ids
E. coli
7 87
0.9 91
1 66
3 261
9 14
4 Leaked
.2 8570
7 4080
5 579
.9 3180
.4 3500
rlyReport
Page|32
Total coliform
292
32550
1986
6310
218
Leaked
34480
28510
13330
36090
43520
B
Ja
D
sco
11/
11/
11/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
/12/2013 11/
10:56 1
11:35 1
12:15 1
13:03 1
13:35 1
/19/2013 11/
9:20 1
9:45 1
10:05 1
10:35 1
10:55 1
/26/2013 11/
10:35 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
/12/2013
16:28 Sp
16:28 Ups
f
16:28 Ups
b
16:28 Dow
b
16:28 Dow
f
/19/2013
14:35 Sp
14:35 Ups
f
14:35 Ups
b
14:35 Dow
b
14:35 Dow
f
/26/2013
14:40 Sp
onTeam
mple cation
DissoP
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
olved P
Total P
006 0.022
011 0.010
012 0.014
012 0.012
011 0.010
007 0.022
010 0.026
011 0.028
011 0.028
009 0.024
007 0.018
P Ammonia‐
N
0.05
0.00
0.09
0.00
0.00
0.02
0.00
0.00
0.00
0.02
0.00
Nitrate‐N T
2.449
0.169
0.221
0.295
0.242
3.063
0.123
0.175
0.231
0.172
1.69
Total N Tot
suspesoli
2.61 8.
0.22 1.
0.33 1.
0.34 0.
0.31 0.
3.06 4.
0.22 0.
0.32 0.
0.34 0.
0.28 1.
1.70 4.
Quarter
tal nded ids
E. coli
9 48
0 45
4 36
5 21
0 24
4 579
7 435
3 172
5 238
0 194
5 86
rlyReport
Page|33
Total coliform
2750
1986
1733
1046
>2419
9880
2400
>2419
2419
4410
1553
B
Ja
D
sco
12
12/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
10:45 1
11:06 1
11:30 1
11:45 1
2/3/2013 12/
8:30 1
8:45 1
9:00 1
9:15 1
9:35 1
/17/2013 12/
9:35 1
10:00 1
10:10 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
14:40 Ups
f
14:40 Ups
b
14:40 Dow
b
14:40 Dow
f
/3/2013
13:23 Sp
13:23 Ups
f
13:23 Ups
b
13:23 Dow
b
13:23 Dow
f
/17/2013
14:03 Sp
14:03 Ups
f
14:03 Ups
b
onTeam
mple cation
DissoP
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
After snow melt
pring 0.0
stream farm
0.0
stream barn
0.0
olved P
Total P
013 0.018
014 0.016
014 0.018
013 0.016
007 0.046
007 0.012
009 0.012
010 0.018
006 0.012
t
007 0.042
010 0.036
011 0.032
P Ammonia‐
N
0.00
0.00
0.03
0.00
0.04
0.00
0.00
0.00
0.00
0.05
0.06
0.02
Nitrate‐N T
0.135
0.190
0.300
0.231
1.048
0.152
0.210
0.295
0.225
0.367
0.180
0.379
Total N Tot
suspesoli
0.14 0.
0.20 0.
0.33 1.
0.24 1.
1.37 26
0.25 0.
0.28 0.
0.35 0.
0.28 0.
0.65 2.
0.27 1.
0.48 0.
Quarter
tal nded ids
E. coli
4 77
7 249
3 40
2 36
.9 25
5 27
3 29
6 248
5 12
0 248.1
2 248.1
7 157.6
rlyReport
Page|34
Total coliform
1203
1986
613
2419
1986
435
548
687
>2419
2419.2
2419.2
>2419.2
B
Ja
D
sco
1/
1/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
10:30 1
10:50 1
/2/2014 1/
10:45 1
10:55 1
11:10 1
11:25 1
11:50 1
/7/2014 1/
10:10 1
10:20 1
10:30 1
10:50 1
11:10 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
14:03 Dow
b
14:03 Dow
f
/2/2014
14:19 Sp
14:19 Ups
f
14:19 Ups
b
14:19 Dow
b
14:19 Dow
f
/7/2014
13:43 Sp
13:43 Ups
f
13:43 Ups
b
13:43 Dow
b
13:43 Dow
f
onTeam
mple cation
DissoP
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
olved P
Total P
008 0.032
008 0.032
006 0.024
009 0.022
012 0.024
012 0.024
012 0.036
008 0.024
014 0.022
017 0.022
015 0.022
015 0.028
P Ammonia‐
N
0.03
0.00
0.05
0.01
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.00
Nitrate‐N T
0.393
0.325
3.348
0.223
0.437
0.543
0.485
2.364
0.204
0.363
0.497
0.413
Total N Tot
suspesoli
0.50 1.
0.43 2.
3.24 0.
0.25 0.
0.47 0.
0.58 0.
0.54 0.
2.32 1.
0.27 0.
0.43 0.
0.54 1.
0.46 0.
Quarter
tal nded ids
E. coli
6 127.4
1 148.3
5 ND
7 ND
3 ND
8 ND
8 ND
3 20.9
8 66.3
3 24.3
1 21.1
2 18.3
rlyReport
Page|35
Total coliform
2419.2
>2419.2
ND
ND
ND
ND
ND
1413.6
307.6
344.8
290.9
325.5
B
Ja
D
sco
1/
1/
1/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
/14/2014 1/1
11:35 1
12:15 1
11:50 1
12:50 1
13:15 1
/21/2014 1/2
8:10 1
8:30 1
8:20 1
8:45 1
9:05 1
/29/2014 1/2
10:20 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
14/2014
15:35 Sp
15:35 Ups
f
15:35 Ups
b
15:35 Dow
b
15:35 Dow
f
21/2014
15:00 Sp
15:00 Ups
f
15:00 Ups
b
15:00 Dow
b
15:00 Dow
f
29/2014
14:15 Sp
onTeam
mple cation
DissoP
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
olved P
Total P
010 0.042
008 0.028
008 0.030
008 0.028
008 0.026
008 0.006
009 0.010
010 0.010
011 0.012
010 0.014
009 0.024
P Ammonia‐
N
0.00
0.01
0.03
0.02
0.05
0.02
0.00
0.01
0.01
0.01
0.00
Nitrate‐N T
1.974
0.156
0.211
0.332
0.310
2.107
0.130
0.211
0.339
0.301
0.851
Total N Tot
suspesoli
2.09 2.
0.25 0.
0.73 0.
0.43 0.
0.39 0.
2.10 0.
0.22 0.
0.28 0.
0.45 1.
0.36 0.
0.86 1.
Quarter
tal nded ids
E. coli
3 24.3
3 151.5
9 238.2
5 156.5
5 95.9
9 5.2
0 55.7
3 51.2
0 49.6
5 131.3
4 3.1
rlyReport
Page|36
Total coliform
1732.9
980.4
920.8
1119.9
1299.7
613.1
290.9
488.4
249.9
410.6
325.5
B
Ja
D
sco
2/
2/
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
10:40 1
10:30 1
11:00 1
/13/2014 2/1
8:30 1
8:50 1
8:40 1
9:10 1
/19/2014 2/1
9:15 1
10:17 1
9:30 1
11:30 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
14:15 Ups
f
14:15 Ups
b
14:15 Dow
f
13/2014
13:22 Sp
13:22 Ups
f
13:22 Ups
b
13:22 Dow
f
19/2014
14:36 Sp
14:36 Ups
f
14:36 Ups
b
14:36 Dow
f
onTeam
mple cation
DissoP
stream farm
0.0
stream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream farm
0.0
Base flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream farm
0.0
olved P
Total P
007 0.028
007 0.024
007 0.024
009 0.024
009 0.016
011 0.014
009 0.014
006 0.020
008 0.018
009 0.018
007 0.016
P Ammonia‐
N
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.00
Nitrate‐N T
0.125
0.195
0.282
0.654
0.107
0.135
0.241
0.574
0.048
0.070
0.109
Total N Tot
suspesoli
0.15 0.
0.24 0.
0.28 0.
0.73 5.
0.15 0.
0.23 0.
0.28 0.
0.62 0.
0.10 0.
0.15 0.
0.17 0.
Quarter
tal nded ids
E. coli
6 10.9
0 28.2
0 <1
1 <1
9 68.9
9 31.4
4 9.8
8 1.0
4 111.9
5 45.5
3 8.5
rlyReport
Page|37
Total coliform
248.1
290.9
275.0
461.1
238.2
260.2
290.9
365.4
325.5
235.9
272.3
B
Ja
D
sco
2
BigCreekResea
anuary1toMar
Date & time
sample ollected
Daterecelab
2/27/14 2/
10:40 1
11:03 1
11:40 1
12:22 1
arch&Extensio
rch31,2014
e & time eived @ oratory
Saloc
/27/14 Bas
15:10 Sp
15:10 Ups
f
15:10 Ups
b
15:10 Dow
f
onTeam
mple cation
DissoP
se flow
pring 0.0
stream farm
0.0
stream barn
0.0
nstream farm
0.0
olved P
Total P
007 0.106
008 0.022
008 0.016
007 0.014
P Ammonia‐
N
0.06
0.02
0.00
0.00
Nitrate‐N T
0.594
0.066
0.084
0.112
Total N Tot
suspesoli
0.82 70
0.22 2.
0.11 0.
0.16 0.
Quarter
tal nded ids
E. coli
0 <1
1 29.5
3 14.8
6 2.00
rlyReport
Page|38
Total coliform
307.6
209.8
235.9
547.5
B
r
9/
U
D
9/
Sp
U
D
9/
Sp
U
D
10
Sp
U
D
10
Sp
BigCreekRe
January1
The w
boundary
Table 5.
Sample location relative to
farm
/12/2013 Ba
Upstream
Downstream
/20/2013 Ba
pring
Upstream
Downstream
/24/2013 Ba
pring
Upstream
Downstream
0/1/2013 Ba
pring
Upstream
Downstream
0/9/2013 Ba
pring
esearch&Ex
toMarch31
water quality
y of the permi
Water qualitFar
Dissolved P
‐ ‐ ‐
ase flow
0.016
0.010
ase flow
0.006
0.009
0.013
ase flow
0.004
0.021
0.007
ase flow
0.001
0.011
0.009
ase flow
0.011
xtensionTe
1,2014
data in Table
itted fields of
ty analyses am boundary
Total P
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.030
0.022
0.020
0.022
0.022
0.024
0.140
0.028
0.162
0.038
0.034
0.054
eam
e 4 for the mo
f the C&H Far
t the spring aof permitted
AmmoniaN
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.06
0.04
0.03
0.03
0.05
0.00
0.03
0.01
0.00
0.02
0.02
0.00
onitored sprin
rm only is give
and in Big Cred land applica
a‐ Nitrate‐N
mg/L ‐ ‐ ‐ ‐ ‐
0.367
0.396
0.384
0.247
0.442
0.122
0.444
0.511
0.108
0.236
0.514
0.088
ng and Big Cr
en in Table 5.
eek upstreamation fields (s
Total N
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.50
0.62
0.50
0.36
0.53
0.35
2.20
0.58
0.41
0.34
0.65
0.28
Qu
reek above an
.
m and downstsee Map 12).
Total suspended
solids
‐ ‐ ‐ ‐
3.0
1.7
4.7
1.1
1.1
50.0
17.9
1.5
89.2
2.2
3.6
29.1
uarterlyRep
Page
nd below the
tream of the
E. coli
‐ ‐ ‐ MPN/1
6
16
73
81
548
9
39
5
4
8
2620
3
port
e|39
C&H
Total coliform
00 mL ‐ ‐ ‐
>2420
>2420
5040
9870
17230
>2420
1120
>2420
920.8
1300
10810
1413.6
B
r
U
D
1
Sp
U
D
Sp
U
D
Sp
U
D
Sp
U
D
Sp
U
BigCreekRe
January1
Sample location relative to
farm
Upstream
Downstream
10/15/2013 S
pring
Upstream
Downstream
10/22/2013
pring
Upstream
Downstream
10/31/2013
pring
Upstream
Downstream
11/6/2013
pring
Upstream
Downstream
11/12/2013
pring
Upstream
esearch&Ex
toMarch31
Dissolved P
0.016
0.006
Storm flow
0.010
0.018
0.067
Base flow
0.005
0.014
0.012
Base flow
0.003
0.012
0.012
Base flow
0.013
0.032
0.041
Base flow
0.006
0.011
xtensionTe
1,2014
Total P
0.034
0.038
0.250
0.026
0.316
0.086
0.034
0.020
0.404
0.032
0.024
0.130
0.074
0.154
0.022
0.010
eam
AmmoniaN
0.00
0.00
0.15
0.00
0.20
0.10
0.00
0.04
0.14
0.00
0.03
0.10
0.03
0.12
0.05
0.00
a‐ Nitrate‐N
0.497
0.618
0.086
1.024
0.677
0.307
0.345
0.723
0.321
0.242
0.443
0.062
0.432
0.286
2.449
0.169
Total N
0.73
0.77
0.58
1.03
1.07
0.53
0.32
0.76
1.02
0.32
0.45
0.72
0.61
0.60
2.61
0.22
Qu
Total suspended
solids
7.1
13.6
66.9
1.1
101.1
36.4
0.3
0.7
400.9
1.1
1.4
21.2
4.7
28.4
8.90
1.00
uarterlyRep
Page
E. coli
11
28
1401
759
1334
1733
186
87
91
66
Leaked
8570
4080
3500
48
45
port
e|40
Total coliform
2419.6
3450.0
19863.0
>2419.6
19863.0
>2419.6
299.0
292.0
32550.0
1986.3
Leaked
34480.0
28510.0
43520.0
2750.0
1986.3
B
r
D
Sp
U
D
Sp
U
D
Sp
U
D
12
Sp
U
D
1/
Sp
U
D
BigCreekRe
January1
Sample location relative to
farm
Downstream
11/19/2013
pring
Upstream
Downstream
11/26/2013
pring
Upstream
Downstream
12/3/2013
pring
Upstream
Downstream
2/17/2013 A
pring
Upstream
Downstream
/2/2014 Bas
pring
Upstream
Downstream
esearch&Ex
toMarch31
Dissolved P
0.011
Base flow
0.007
0.010
0.009
Base flow
0.007
0.013
0.013
Base flow
0.007
0.007
0.006
After snow m
0.007
0.010
0.008
e flow
0.006
0.009
0.012
xtensionTe
1,2014
Total P
0.010
0.022
0.026
0.024
0.018
0.018
0.016
0.046
0.012
0.012
melt
0.042
0.036
0.032
0.024
0.022
0.036
eam
AmmoniaN
0.00
0.02
0.00
0.02
0.00
0.00
0.00
0.04
0.00
0.00
0.05
0.06
0.00
0.05
0.01
0.00
a‐ Nitrate‐N
0.242
3.063
0.123
0.172
1.69
0.135
0.231
1.048
0.152
0.225
0.367
0.180
0.325
3.348
0.223
0.485
Total N
0.31
3.06
0.22
0.28
1.70
0.14
0.24
1.37
0.25
0.28
0.65
0.27
0.43
3.24
0.25
0.54
Qu
Total suspended
solids
0.0
4.4
0.7
1.0
4.5
0.4
1.2
26.9
0.5
0.5
2.0
1.2
2.1
0.5
0.7
0.8
uarterlyRep
Page
E. coli
24
579
435
194
86
77
36
25
27
12
248.1
248.1
148.3
ND
ND
ND
port
e|41
Total coliform
>2419.2
9880.0
2400.0
4410.0
1553.1
1203.3
2419.2
1986.3
435.2
>2419.2
2419.2
2419.2
>2419.2
ND
ND
ND
B
r
1/
Sp
U
D
1/
Sp
U
D
1/
Sp
U
D
1/
Sp
U
D
2/
Sp
U
D
2/
BigCreekRe
January1
Sample location relative to
farm
/7/2014 Bas
pring
Upstream
Downstream
/14/2014 Ba
pring
Upstream
Downstream
/21/2014 Ba
pring
Upstream
Downstream
/29/2014 Ba
pring
Upstream
Downstream
/13/2014 Ba
pring
Upstream
Downstream
/19/2014 Ba
esearch&Ex
toMarch31
Dissolved P
e flow
0.008
0.014
0.015
ase flow
0.010
0.008
0.008
ase flow
0.008
0.009
0.010
ase flow
0.009
0.007
0.007
ase flow
0.009
0.009
0.009
ase flow
xtensionTe
1,2014
Total P
0.024
0.022
0.028
0.042
0.028
0.026
0.006
0.010
0.014
0.024
0.028
0.024
0.024
0.016
0.014
eam
AmmoniaN
0.00
0.02
0.00
0.00
0.01
0.05
0.02
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
a‐ Nitrate‐N
2.364
0.204
0.413
1.974
0.156
0.310
2.107
0.130
0.301
0.851
0.125
0.282
0.654
0.107
0.241
Total N
2.32
0.27
0.46
2.09
0.25
0.39
2.10
0.22
0.36
0.86
0.15
0.28
0.73
0.15
0.28
Qu
Total suspended
solids
1.3
0.8
0.2
2.3
0.3
0.5
0.9
0.0
0.5
1.4
0.6
0.0
5.1
0.9
0.4
uarterlyRep
Page
E. coli
20.9
66.3
18.3
24.3
151.5
95.9
5.2
55.7
131.3
3.1
10.9
<1
<1
68.9
9.8
port
e|42
Total coliform
1413.6
307.6
325.5
1732.9
980.4
1299.7
613.1
290.9
410.6
325.5
248.1
275.0
461.1
238.2
290.9
B
r
Sp
U
D
2/
Sp
U
D
BigCreekRe
January1
Sample location relative to
farm
pring
Upstream
Downstream
/27/14
pring
Upstream
Downstream
ND is no d
esearch&Ex
toMarch31
Dissolved P
0.006
0.008
0.007
Base flow
0.007
0.008
0.007
data collected
xtensionTe
1,2014
Total P
0.020
0.018
0.016
0.106
0.022
0.014
d.
eam
AmmoniaN
0.02
0.00
0.00
0.06
0.02
0.00
a‐ Nitrate‐N
0.574
0.048
0.109
0.594
0.066
0.112
Total N
0.62
0.10
0.17
0.82
0.22
0.16
Qu
Total suspended
solids
0.8
0.4
0.3
70
2.1
0.6
uarterlyRep
Page
E. coli
1.0
111.9
8.5
<1
29.5
2.00
port
e|43
Total coliform
365.4
325.5
272.3
307.6
209.8
547.5
B
BigCreekRe
January1
Future
1. Instru
2. Comp
down
that h
we ha
real‐t
3. Deplo
locati
dioxid
storm
of res
to als
surve
locate
EpCO
4. Interp
5. Conti
autos
stream
samp
6. Condu
traini
7. Period
deter
8. Deter
applic
monit
ManureEvaluat
Cont
economic
1. Sep
2. Ret
3. Exp
esearch&Ex
toMarch31
ePlanofW
ument Field 1
plete installat
nstream of the
has been cond
ave funded to
ime flow info
oy sondes at t
ons to contin
de (EpCO2), el
m event fluctu
spiration and
o identify pos
y downstream
e potential sit
2 will increase
pret GPR info
nue to collect
samplers and
ms, for analys
les).
uct dye‐trace
ng in conduct
dically determ
mine yield (d
rmine nutrien
cation via ma
toring area.
eTreatmeteCostBen
tinue current
cally viable, o
parating manu
aining sufficie
orting excess
xtensionTe
1,2014
Work
2 with piezom
ion of autom
e C&H Farm.
ducted since
o have a perm
ormation, to c
the spring and
nuously deter
lectrical cond
uations of wat
photosynthe
ssible sources
m between u
tes where wa
e (and pH will
rmation from
t runoff, sprin
manually col
sis of N, P, se
er tests on the
ting dye‐trace
mine plant up
ry‐matter ma
nt application
nure applicat
entviaSolinefitsofA
discussions w
ptions to mod
ure liquids an
ent nitrogen t
s P off the far
eam
meters and su
atic flow and
These sites c
early Septem
manent gaugin
conform with
d above perm
mine dissolve
ductivity (EC),
ter EpCO2, DO
sis linked to c
s of new and
pper and low
ter is enterin
l drop), with t
m Field 12 com
ng, and stream
lect baseflow
diment, and b
e C&H Farm in
er tests.
ptake by colle
ass for a pre‐d
rate by dete
tion and dete
idsandChAlternative
with the owne
dify current m
d solids along
to meet crop
m;
urface runoff
water sampl
coordinate wi
mber. This is b
ng station dow
all USGS gau
manent USGS
ed oxygen (DO
and tempera
O, EC, and tem
changing nutr
old water at
wer sampling p
ng the Creek f
the input of s
mpleted this q
m samples af
w samples eve
bacteria (E. co
n cooperation
cting plant an
determined a
rmining nutri
rmine volum
hemicalSeeManureM
ers of the C&
manure mana
g with their d
needs;
monitoring e
ling equipme
ith the ongoin
being done in
wnstream of
uging sites acr
gauging stati
O), excess pa
ature of the w
mperature ca
rient status a
these locatio
points in Big C
from the surr
spring water i
quarter and p
fter each rain
ery two week
oli and total c
n with a Geol
nd hay sampl
area).
ient content o
e of effluent
eparation:Manageme
H Farm to ex
agement prac
differential ma
Qu
equipment as
nt on Big Cre
ng weekly ba
n partnership
the C&H Farm
ross the State
ions on Big Cr
artial pressure
water. Diurn
n be used to
nd organic m
ons. Similarly
Creek under
ounding land
into Big Creek
present next q
fall event fro
ks from the w
coliform from
ogist with ex
les for tissue
of swine efflu
being applied
ACaseStuentOption
plore potenti
ctices in the g
anagement;
uarterlyRep
Page
s on Field 1.
ek upstream
seflow sampl
with USGS, w
m that provid
e.
reek sampling
e of carbon
al, seasonal,
examine the
matter loading
, a longitudin
baseflow, can
dscape. That
k.
quarter.
m the
ell, spring, an
m baseflow gr
perience and
analysis and
uent before la
d to known
udytons
ial long‐term,
general areas
port
e|44
and
ling
who
des
g
and
rates
g and
nal
n
is,
nd
rab
d
and
,
of:
B
BigCreekRe
January1
4. Mit
5. Not
6. Ope
The p
the option
Me
off‐
Sel
tha
For t
assessme
will be uti
especially
discussion
tests will g
esearch&Ex
toMarch31
igating off‐sit
t exceeding th
erating within
project will id
ns will include
echanical sepa
‐farm transpo
ective applica
at minimizes a
he managem
nt of their im
ilized in this p
y true when e
ns developme
guide decisio
xtensionTe
1,2014
te odor;
he current ph
n the constrai
dentify manag
e but not be l
aration manu
ort of separat
ation of highe
any loss of nu
ment options i
mplementation
process. Howe
valuating ma
ent of field ch
ns that may l
eam
hysical, econo
ints of the ap
gement optio
limited to:
ure solids from
ted solids; an
er P content s
utrient loss.
dentified, the
n impacts ma
ever, there w
nure solid‐liq
hemical tests
ead to additi
omic, labor, an
propriate env
ons to meet th
m liquids with
d
slurries and lo
eir initial and
ade. Available
will be a need
quid separatio
and lab analy
onal larger sc
nd managem
vironmental r
he above obje
h or without c
ower P conte
long‐term co
e literature an
for laborator
on and/or che
ysis will begin
cale impleme
Qu
ent resource
regulations.
ectives. It is a
chemicals as a
nt liquids to d
osts will be es
nd other infor
ry and onsite
emical use. B
n soon. The re
entation trials
uarterlyRep
Page
s of the farm
anticipated th
a precursor fo
different field
stimated and
rmation resou
tests/trials. T
ased on curre
esults of these
s.
port
e|45
; and
hat
or
ds
an
urces
This is
ent
e
BigC
J
CreekResearch
January1toMa
Lab Num
2442
2442
2443
2443
2444
2444
2445
2445
2446
2446
2447
2447
2448
2448
2449
2449
2450
2450
2451
2451
2452
2453
2453
2454
h&ExtensionT
arch31,2014
mber Point
22 9
27 10
32 11
38 13
43 17
49 18
52 19
56 20
61 21
66 22
72 25
76 26
80 27
86 28
91 29
97 30
02 33
08 34
13 35
19 37
24 38
30 41
35 42
40 43
Team
Table 6. Soi
t pH P
5.9 13
6.0 14
5.6 14
6.0 6
5.7 11
5.9 14
5.7 12
5.7 10
5.8 6
5.3 7
5.5 6
5.6 12
5.8 10
5.8 4
5.6 3
5.6 5
5.3 5
6.1 4
6.0 3
5.8 6
5.8 5
5.9 4
6.0 3
6.2 2
l analyses of 0 to
P K
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
38 115
43 196
47 88
5 70 1
17 117
47 223
26 174
01 96 1
1 61 1
1 56
0 57
28 202
09 69
5 54 1
9 60
3 212
3 29
3 76 1
7 81 1
3 62 1
2 45
3 50 1
0 70 1
9 67 1
o 4 inch samples
Ca Mg
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
776 81
763 79
681 68
1621 98
721 72
726 93
608 94
1169 101
1367 82
734 67
788 62
690 80
956 75
1441 87
993 73
873 69
743 43
1530 83
1207 90
1039 65
828 49
1318 49
1781 105
1767 83
collected from F
Na S
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
10 18
7 14
13 17
9 13
10 15
12 17
7 14
9 17
10 14
9 13
8 17
7 17
10 16
12 14
9 12
14 12
9 10
9 12
10 13
13 18
9 15
14 15
14 15
17 14
ield 12.
Fe Mn
mg/kg ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
149 186
138 226
155 245
128 18
146 187
145 23
154 197
151 177
153 168
261 157
107 218
151 172
143 159
117 170
151 193
155 165
167 13
134 184
102 143
118 190
92 119
101 185
102 98
108 173
Quarterly
P
n Cu
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
6 1.2
6 0.9
5 1.2
1 1.4
7 0.8
1 0.8
7 0.8
7 1.3
8 1.2
7 0.7
8 0.8
2 1.0
9 0.9
0 1.2
3 1.0
5 0.7
1 0.7
4 1.4
3 1.0
0 1.6
9 0.9
5 1.5
8 1.6
3 1.5
yReport
Page|46
Zn B
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
3.2 0.2
3.2 0.2
2.4 0.1
3.7 0.3
2.1 0.1
2.7 0.2
2.6 0.1
2.7 0.2
2.4 0.2
2.5 0.1
1.3 0.1
2.6 0.1
2.1 0.3
1.8 0.2
2.1 0.1
2.6 0.1
2.2 0.0
3.3 0.2
1.9 0.1
2.1 0.1
3.0 0.1
1.4 0.2
5.7 0.2
1.5 0.3
BigC
J
CreekResearch
January1toMa
Lab Num
2454
2455
2455
2456
2456
2456
2457
2458
2458
2459
2459
2460
2460
2461
2461
2462
Mean, mg/
Minimum,
Maximum,
Standard d
Coefficient
h&ExtensionT
arch31,2014
mber Point
46 44
51 45
57 46
62 47
63 49
69 50
74 51
80 52
85 53
91 54
96 57
02 58
07 59
12 60
17 61
22 62
/kg
mg/kg
, mg/kg
deviation, mg/kg
t of variation, %
Team
t pH P
5.6 7
5.8 3
5.8 4
5.9 4
6.1 2
5.9 1
6.3 1
6.3 3
6.1 3
6.1 3
6.0 2
6.0 3
5.9 3
6.0 5
6.0 3
6.0 9
5.86 6
5.30 1
6.30 14
0.23 4
3.97 6
P K
3 88 1
0 47 1
7 212
2 76 1
4 59 1
9 54 1
7 56 1
0 43 1
3 54 1
2 43
6 53 1
6 58 1
9 40
2 98 1
4 72 1
7 282 1
3 92 1
7 29
47 282 1
0 62
3 67
Ca Mg
1048 86
1143 81
820 52
1838 117
1953 84
1758 77
1908 85
1537 55
1416 56
970 57
1120 38
1338 63
853 56
1357 106
1453 85
1723 148
1184 77
608 38
1953 148
405 21
34 28
Na S
8 15
19 11
10 13
11 15
12 13
19 12
17 10
12 10
13 10
15 8
10 8
9 10
9 9
12 12
11 13
12 16
11 13
7 8
19 18
3 3
27 20
Fe Mn
136 154
113 149
133 12
96 96
83 64
87 84
87 96
100 109
102 110
115 106
108 102
101 78
116 103
107 88
118 122
139 69
127 148
83 64
261 245
32 48
25 32
Quarterly
P
n Cu
4 1.1
9 1.1
1 0.7
6 1.4
4 1.5
4 1.6
6 1.6
9 1.5
0 1.5
6 1.2
2 1.7
8 1.3
3 1.1
8 1.7
2 1.3
9 1.5
8 1.2
4 0.7
5 1.7
8 0.3
2 26.4 3
yReport
Page|47
Zn B
2.2 0.1
2.8 0.2
2.0 0.2
2.4 0.3
1.5 0.3
1.1 0.2
1.8 0.2
1.4 0.1
1.8 0.1
1.5 0.1
1.5 0.1
1.3 0.1
1.5 0.1
1.6 0.2
1.7 0.2
2.6 0.3
2.2 0.2
1.1 0.0
5.7 0.3
0.8 0.1
37.6 46.6
BigC
J
CreekResearch
January1toMa
Lab Nu
2442
2442
2443
2443
2444
2445
2445
2445
2446
2446
2447
2447
2448
2448
2449
2449
2450
2450
245
2452
2452
2453
2453
2454
h&ExtensionT
arch31,2014
mber Point
23 9
28 10
34 11
39 13
44 17
50 18
53 19
58 20
62 21
67 22
73 25
77 26
82 27
87 28
92 29
98 30
03 33
09 34
14 35
20 37
25 38
31 41
36 42
42 43
Team
Table 7. Soi
t pH P
6.4 4
5.8 7
5.9 8
6 3
5.8 6
5.6 10
5.7 6
5.7 3
5.9 2
5.3 6
5.8 3
5.7 8
5.9 7
6.1 1
5.8 1
5.8 2
6 3
6.1 2
6.1 1
5.9 4
6 2
6.3 3
5.9 1
6.4 1
l analyses of 4 to
P K
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
7 47
3 112
1 47
2 56 1
9 64
02 106
2 127
6 70 1
7 62 1
2 37
2 41
8 115
7 45
3 73 1
7 55 1
6 45
8 27
1 54 1
7 65 1
7 49 1
3 42
2 43 1
8 77 2
5 59 1
o 8 inch samples
Ca Mg
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
650 26
663 39
678 38
1447 58
670 43
682 51
601 49
1307 57
1489 52
488 28
713 24
723 57
879 41
1778 52
1315 40
767 33
675 24
1670 65
1297 63
1171 48
785 29
1257 32
2257 111
1681 50
collected from F
Na S
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
6 11
6 11
9 12
9 11
8 11
16 14
9 11
10 14
15 11
8 8
7 12
7 14
8 12
12 11
13 11
10 8
6 6
8 9
11 10
13 15
8 11
13 12
16 15
19 11
ield 12.
Fe M
mg/kg ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
94 10
110 14
123 17
117 98
100 11
128 15
108 10
106 72
105 82
160 10
80 11
121 11
116 11
90 64
119 14
105 78
121 81
111 14
97 11
98 11
73 67
90 13
107 75
92 11
Quarterly
P
n Cu
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
3 0.7
5 0.8
7 1.1
8 1.4
9 0.7
4 0.8
5 0.7
2 1.4
2 1.5
1 0.5
4 0.7
1 0.8
8 0.9
4 1.1
7 1.3
8 0.5
1 0.6
4 1.5
7 1.1
2 1.7
7 0.6
2 1.7
5 2
5 1.5
yReport
Page|48
Zn B
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.8 0
2.2 0.1
2.4 0.1
1.7 0.2
0.9 0
1.6 0.1
1.2 0
1 0.2
1 0.1
0.9 0
0.4 0
1.2 0.1
1.1 0.1
0.5 0.2
1.1 0.2
0.8 0
1 0
1.7 0.2
2.8 0
9.6 0.1
0.4 0
3.4 0.1
2.2 0.3
0.8 0.2
BigC
J
CreekResearch
January1toMa
Lab Nu
2454
2455
2455
2456
2457
2457
2458
2458
2459
2459
2460
2460
246
246
2462
Mean, mg
Minimum
Maximum
Standard
Coefficien
h&ExtensionT
arch31,2014
mber Point
47 44
52 45
58 46
64 49
70 50
75 51
81 52
86 53
92 54
97 57
03 58
08 59
14 60
18 61
23 62
g/kg
m, mg/kg
m, mg/kg
deviation, mg/kg
nt of variation, %
Team
t pH P
5.3 3
5.9 1
6 3
6.1 1
5.9 1
6.3 9
6.2 2
6.2 1
6.2 1
6.1 3
6.1 2
6 2
6.1 2
6.1 1
5.9 4
5.96 3
5.30 9
6.40 10
g 0.25 2
% 4.14 6
P K
9 82
7 54 1
5 116
5 67 2
2 51 1
9 79 2
2 49 1
6 66 1
9 60 1
3 63 1
8 64 1
4 42
3 92 1
7 60 1
8 202 1
6 68 1
9 27
02 202 2
4 32
5 47
Ca Mg
926 66
1404 70
630 28
2386 81
1844 68
2453 105
1419 54
1631 59
1552 47
1375 46
1360 67
848 36
1432 102
1440 67
1841 116
1235 54
488 24
2453 116
523 23
42 43
Na S
9 15
13 11
9 9
19 14
17 11
15 10
13 9
11 10
12 8
15 9
10 9
8 7
12 12
13 11
12 14
11 11
6 6
19 15
4 2
32 20
Fe M
110 10
103 12
99 77
87 30
72 44
92 78
99 89
97 81
113 85
104 79
94 53
108 96
101 55
95 10
100 44
104 97
72 30
160 17
16 33
15 34
Quarterly
P
n Cu
6 1.2
7 1.4
7 0.6
0 1.6
4 1.3
8 1.8
9 1.5
1 1.5
5 1.6
9 1.8
3 1.3
6 1.2
5 1.6
0 1.5
4 1.6
7 1.2
0 0.5
7 2.0
3 0.4
4 35.1 1
yReport
Page|49
Zn B
1 0
1 0.2
0.7 0
0.8 0.3
0.7 0.2
1.4 0.4
1.1 0.1
0.9 0.1
1.3 0.2
1.8 0.1
0.8 0.1
0.9 0
0.6 0.1
1 0.1
1.1 0.2
1.4 0.1
0.4 0.0
9.6 0.4
1.5 0.1
104.2 89.1
BigC
J
CreekResearch
January1toMa
Lab Nu
2442
2442
2443
2444
2444
2445
2445
2445
2446
2446
2447
2447
2448
2448
2449
2449
2450
245
245
2452
2452
2453
2453
2454
h&ExtensionT
arch31,2014
mber Point
24 9
29 10
35 11
40 13
46 17
51 18
54 19
59 20
63 21
68 22
74 25
78 26
83 27
88 28
94 29
99 30
04 33
10 34
15 35
21 37
26 38
32 41
37 42
43 43
Team
Table 8. Soil
t pH P
6 8
6 4
6.2 4
6.1 2
5.8 5
5.8 5
5.8 4
5.9 2
5.8 3
5.2 3
5.9 2
5.7 4
6.1 3
6.1 1
6 1
5.9 1
6.1 3
6.1 1
6.3 1
5.9 2
6 1
6.1 2
5.9 1
6.5 1
analyses of 8 to
P K
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
82 63
42 96
44 49
22 78
50 77
53 65
45 106
21 80
2 72
9 46
22 52
46 128
4 52
13 86
10 74
11 57
0 34
14 70
10 82
28 48
19 40
26 52
14 79
12 75
12 inch samples
Ca Mg
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
713 45
607 29
716 24
1755 72
681 40
673 34
712 39
1779 56
1493 49
481 23
781 23
681 42
1121 31
1787 76
1760 48
1297 40
720 25
2050 78
1722 75
1104 44
643 22
1505 34
2443 118
1849 53
collected from F
Na S
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
7 14
7 9
8 8
20 11
9 9
6 10
8 9
11 15
12 13
8 8
9 9
9 12
8 11
13 11
15 9
13 13
8 5
11 9
16 11
10 12
9 7
13 12
18 15
18 10
Field 12.
Fe M
mg/kg ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
101 13
95 10
107 11
103 7
107 8
101 9
99 7
104 5
102 4
126 9
90 9
94 7
93 7
103 9
104 9
89 4
124 9
105 11
93 7
88 6
69 4
91 9
103 4
90 6
Quarterly
P
Mn Cu
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
39 1
04 0.6
17 0.8
73 1.5
88 0.4
91 0.6
78 0.6
53 1.4
48 1.4
95 0.6
93 0.5
70 0.7
72 1.1
90 0.9
96 1.4
49 0.9
96 0.7
19 1.8
71 1.3
60 1.4
43 0.2
93 2
44 1.9
63 1.6
yReport
Page|50
Zn B
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
1.3 0.1
0.9 0
0.6 0
1.5 0.2
0.9 0
0.5 0
0.3 0
0.7 0.2
0.4 0.1
1.6 0
0.2 0
0.4 0
0.6 0
0.5 0.2
3 0.2
0.4 0.1
1.6 0
1.5 0.2
0.3 0.1
1.3 0.1
0.5 0
2.8 0.2
0.9 0.3
0.5 0.1
BigC
J
CreekResearch
January1toMa
Lab Nu
2454
2455
2455
2456
2457
2457
2458
2458
2459
2459
2460
2460
246
246
2462
Mean, mg
Minimum
Maximum
Standard
Coefficien
h&ExtensionT
arch31,2014
mber Point
48 44
54 45
59 46
66 49
71 50
76 51
82 52
87 53
93 54
98 57
04 58
09 59
15 60
19 61
24 62
g/kg
m, mg/kg
m, mg/kg
deviation, mg/kg
nt of variation, %
Team
t pH P
5.2 1
6.1 1
6 2
6.1 1
5.9 1
6.3 7
6 2
6.1 1
6.2 1
5.9 3
6.1 3
6.1 2
6.2 2
6.1 1
5.9 1
5.9
5.2
6.5
g 0.2
% 4.0
P K
18 104
11 74
24 71
16 63
10 69
7 88
20 60
18 71
13 61
9 65
1 76
25 53
25 85
10 71
19 164
98 26
20 7
50 82
24 16
08 61
Ca Mg
1219 75
1752 79
936 41
2099 66
2043 78
2536 104
1768 77
1493 74
1805 54
1301 51
1468 69
942 42
1559 108
1899 90
1848 109
73 1378
34 481
164 2536
24 562
33 41
Na S
12 19
15 11
10 10
21 15
22 15
19 10
17 13
17 9
11 9
14 9
12 9
10 7
13 11
14 13
12 15
57 12
22 6
118 22
26 4
46 34
Fe M
106 7
108 11
98 8
90 1
86 2
98 5
100 6
100 5
105 5
99 5
96 4
120 10
105 4
87 6
88 2
11 9
5 6
19 12
3 1
26 1
Quarterly
P
Mn Cu
73 1.3
12 1.5
86 1
13 1.6
21 1.3
58 1.7
60 1.6
53 1.3
55 1.5
54 1.5
41 1.2
07 1.3
41 1.3
61 1.3
25 1.4
99 72
69 13
26 139
11 29
11 40
yReport
Page|51
Zn B
1.5 0.1
1.3 0.2
0.7 0.1
0.6 0.1
0.5 0.1
0.8 0.3
1.1 0.2
0.7 0.1
1.1 0.2
0.9 0.1
0.5 0.1
1.2 0
0.8 0.1
0.9 0.2
0.5 0.1
1.2 0.9
0.2 0.2
2.0 3.0
0.4 0.6
37.2 65.6
BigC
J
CreekResearch
January1toMa
Lab Numb
24425
24430
24436
24441
24447
24455
24460
24464
24470
24475
24479
24484
24489
24495
24500
24506
24511
24516
24522
24527
24533
24538
24544
24549
h&ExtensionT
arch31,2014
ber Point
9
10
11
13
17
19
20
21
22
25
26
27
28
29
30
33
34
35
37
38
41
42
43
44
Team
Table 9. Soil a
t pH P
6.1 5
6.1 4
6.3 5
6.1 1
5.9 5
6 6
6.1 1
5.3 3
5.2 2
5.9 2
5.8 3
6.2 2
6.1 2
6.3 1
5.7 1
6.1 2
6.4 1
6.1 1
5.8 2
5.6 4
6 2
5.9 1
6.6 1
5.4 1
analyses of 12 to
P K
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0 54
0 101
9 60
9 88
7 79
1 80
4 75
8 80
0 87
8 48
3 185
4 62
3 57
2 82
1 78
9 59
1 78
1 80
7 57
0 56
0 50
1 80 2
8 77
1 85
o 18 inch samples
Ca Mg
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
674 29
656 33
817 28
1909 75
746 39
942 43
1699 57
1308 55
1151 45
616 26
646 35
1349 39
1630 51
1821 66
1674 55
1385 42
1934 85
1765 86
1622 61
644 27
1832 46
2372 116
1703 57
1457 81
s collected from
Na S
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
11 7
8 7
12 6
15 12
12 8
13 7
14 14
14 16
9 16
11 6
8 11
13 10
11 12
16 9
13 15
9 8
13 10
24 12
12 16
13 10
16 12
19 17
14 9
14 17
Field 12.
Fe M
mg/kg ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
107 7
103 8
121 8
99 6
113 6
103 4
93 2
110 4
118 7
89 6
90 5
94 5
100 8
104 7
93 3
144 1
107 8
87 4
87 4
94 3
92 5
100 2
89 4
97 4
Quarterly
P
Mn Cu
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
77 0.5
85 0.4
86 0.6
61 1.2
64 0.2
45 0.3
28 1.2
40 1.2
73 1.3
61 0.1
53 0.5
58 1.3
89 1.3
76 1.2
36 0.8
108 1.3
86 1.6
41 1.1
47 1.5
33 0.2
50 1.9
25 1.6
41 1.3
41 1
yReport
Page|52
Zn B
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.8 0
1 0
0.3 0
0.8 0.3
0.3 0
0.3 0
0.6 0.1
0.4 0
0.6 0.1
0.5 0
0.3 0
0.7 0.1
1 0.2
0.9 0.1
0.6 0
1.1 0.1
2.6 0.2
0.2 0.1
0.4 0.2
2.5 0
3.9 0.2
0.6 0.2
3.7 0.1
0.5 0.1
BigC
J
M
M
M
S
C
CreekResearch
January1toMa
Lab Numb
24555
24560
24567
24572
24578
24583
24588
24594
24599
24605
24610
24616
24620
24625
Mean, mg/kg
Minimum, mg/kg
Maximum, mg/k
Standard deviatio
Coefficient of var
h&ExtensionT
arch31,2014
ber Point
45
46
49
50
51
52
53
54
57
58
59
60
61
62
g
g
on, mg/kg
riation, %
Team
t pH P
6 9
5.7 1
5.8 1
5.9 8
6.2 9
5.4 1
5.6 1
6.1 1
5.9 4
6.3 2
5.9 1
5.7 3
6.1 8
6 1
5.9
5.2
6.6
0.3
5.1
P K
9 79
6 80
1 63
8 70
9 89 2
9 63
8 80
2 67 2
4 68
9 66
4 60
3 84
8 76
3 128
94 23.95 7
20 8.00 4
60 61.00 1
30 15.16 2
13 63.32 3
Ca Mg
1640 79
1440 64
1630 46
1711 70
2387 100
1671 78
1380 86
2121 74
1202 61
1186 54
1730 72
1334 94
1908 97
1740 104
76.61 1458.74
48.00 616.00
85.00 2387.00
23.61 477.93
30.81 32.76
Na S
16 10
13 11
20 16
24 13
22 10
20 17
25 11
15 10
16 8
12 7
16 9
16 12
17 12
22 14
62.00 14.9
26.00 8.00
116.00 25.0
23.68 4.40
38.19 29.4
Fe M
99 6
103 8
91 1
87 2
98 5
111 4
100 4
105 3
101 4
85 2
119 5
106 3
87 5
84 2
95 11.24 10
0 6.00 84
00 17.00 14
0 3.32 12
47 29.58 12
Quarterly
P
Mn Cu
67 1.3
81 1.3
14 1.1
28 1
59 1.7
49 1.7
45 1.1
35 1.4
43 1.2
24 0.6
54 1.5
33 1
51 1.1
25 1.3
0.26 52.95
4.00 14.00
4.00 108.00
2.17 21.94
2.14 41.43
yReport
Page|53
Zn B
1 0.1
0.7 0.1
0.4 0
0.4 0.1
0.9 0.3
0.9 0.1
0.6 0
0.7 0.2
0.5 0
0.5 0
1.1 0.2
0.5 0
0.4 0.1
0.8 0.1
1.08 0.89
0.10 0.20
1.90 3.90
0.46 0.85
42.41 95.44
BigC
J
CreekResearch
January1toMa
Lab Numb
24426
24431
24437
24442
24448
24465
24471
24485
24490
24496
24501
24507
24512
24518
24523
24528
24534
24539
24545
24550
24556
24561
24568
24573
h&ExtensionT
arch31,2014
ber Point
9
10
11
13
17
21
22
27
28
29
30
33
34
35
37
38
41
42
43
44
45
46
49
50
Team
Table 10. Soil
t pH P
6.1 6
6.3 5
6.1 9
6.2 1
5.9 6
5.2 3
5.5 1
6.3 2
6.1 1
6.3 1
5.7 1
6.2 2
6.1 1
5.9 1
6 1
4.9 4
5.9 2
6.1 9
6.5 2
5.3 1
6 1
5.7 1
5.7 3
6 4
analyses of 18 to
P K
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
63 55
58 83
90 71
16 83
62 71
8 79
13 82
28 70
12 93
14 86
17 95
20 66
12 74
16 86
19 62
46 60
21 48
9 79
29 85
13 81
10 85
11 99
6 100
44 62
o 24 inch sample
Ca Mg
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
641 33
761 51
847 49
1586 75
763 41
1153 56
1419 80
1337 43
1877 89
1857 74
1781 61
1646 53
1697 81
1608 90
1479 59
443 30
1837 50
2005 102
1659 77
1342 66
1622 82
1700 67
1682 118
1867 104
es collected from
Na S
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ m
12 6
15 6
16 6
11 11
14 7
17 14
11 13
13 10
19 10
26 8
19 13
10 9
14 9
27 14
13 19
13 18
17 14
17 17
23 7
17 16
18 10
16 9
18 15
13 14
m Field 12.
Fe M
mg/kg ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
117 5
103 4
119 4
88 3
104 3
112 3
100 4
94 3
95 11
101 5
93 2
130 10
92 4
95 4
92 3
102 2
90 2
95 2
84 2
98 2
95 4
107 5
105 12
101 15
Quarterly
P
Mn Cu
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
57 0.3
48 0.3
44 0.4
2 0.8
4 0.1
7 1
40 0.8
9 1.1
14 0.7
57 1.2
22 0.5
04 1.1
45 1.1
42 1.1
1 1.3
28 0.2
26 1.6
21 1.3
27 1.1
28 0.8
45 0.9
53 1
29 1.7
57 1.6
yReport
Page|54
Zn B
‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐
0.6 0
0.5 0
1 0
0.4 0.1
0.4 0
0.4 0
0.4 0.1
0.3 0
0.4 0.1
0.9 0.1
0.3 0
0.6 0.2
2.2 0.1
0.5 0.1
0.7 0.1
0.6 0
0.5 0.2
7 0.1
0.3 0.1
2 0
0.4 0.1
0.4 0.1
2.2 0.2
2.9 0.3
BigC
J
M
M
M
S
C
CreekResearch
January1toMa
Lab Numb
24579
24584
24590
24595
24600
24606
24611
24621
24626
Mean, mg/kg
Minimum, mg/kg
Maximum, mg/k
Standard deviatio
Coefficient of var
h&ExtensionT
arch31,2014
ber Point
51
52
53
54
57
58
59
61
62
g
g
on, mg/kg
riation, %
Team
t pH P
6.2 5
5.8 8
5.7 5
6 3
5.9 5
5.7 7
6.1 10
5.8 8
5.8 1
5.91 3
4.90 8
6.50 10
0.34 2
5.70 7
P K
54 50
83 71
54 43
5 53
55 54
70 46
01 125
8 72
11 98
5 75
8 43
01 125
26 18
74 25
Ca Mg
1643 87
1329 97
968 91
1351 68
1143 78
1064 94
1408 134
1569 66
1558 76
1413 73
443 30
2005 134
397 24
28 32
Na S
13 14
11 14
9 11
10 11
11 11
9 12
9 13
15 12
11 14
15 12
9 6
27 19
5 3
31 29
Fe M
117 15
136 15
154 14
121 14
114 11
140 13
134 13
91 4
84 3
106 7
84 2
154 15
17 4
16 6
Quarterly
P
Mn Cu
58 1.5
51 1.4
43 1.3
42 1.5
14 1
38 1.1
31 1.5
47 0.7
1 0.7
70 1.0
21 0.1
58 1.7
48 0.4
69 43.4 1
yReport
Page|55
Zn B
2.6 0.3
3.4 0.2
3 0.2
2.7 0.2
2 0.2
3 0.1
3.9 0.3
0.3 0.1
0.3 0
1.4 0.1
0.3 0.0
7.0 0.3
1.5 0.1
105.4 86.9
BBigCreekRe
January
The
natio
esearch&Ex
1toMarch3
e Division of
nal origin, re
protected
xtensionTe
31,2014
Agriculture o
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