Water Chemistry of Ten ·Lakescompletes. Le titre exact paraitra au haut du resume de chaque...
Transcript of Water Chemistry of Ten ·Lakescompletes. Le titre exact paraitra au haut du resume de chaque...
SJI ~3 v13 9'~ Water Chemistry of Ten ·Lakes in Southern New Brunswick
·Biological - Station,
·v t. .
. t.
St. Andrews, N. B., EOG 2X --~-- ....,
ARLIS - Alaska Resources Library & Information
August 1980
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, 3211 Providence Drive
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Canadian· Technical Report of Fisheries and Aquatic Sciences No. 962
SH 223 .A3473 no.962
d Canada Gouvemement du Canada ODians P6ches et Oceans
Canadian Technical Report of
Fisheries and Aquatic Sciences
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ARLIS Alaska Resources
Library & Information Services Anchorage, AK
F Aquatic iences 962
August 1980
CHEMl LAKES NEW
by
Fisher and Environmenta Sciences
Department of Fisher and Oceans
logical
st.
This is the one hundred and twenty-seventh Technical Report from
the Rio Stat ion, St. Andrews,
Hinister of Supply and Services Canada
Cat. No. 97-6/962 ISSN 0706-6457
ication:
Can.
ABSTRACT
stry akes in New
The concentrations of various ions are discussed patterns duri the sampling, and local geology.
1980. 25
La concentr·ation des facteur·s ogiques,
, al
stry of ten akes
ver'S ions fait 1 0bjet djune discussion en rei uviosite au cours de la campagne et la geol
Can,. Fish.
on samples ten l Mosquito Lake, Robin Hood
/L HC03-) and had mean surrmer with mean 's of 6. 7-6.
and vlheaton about
concentrations indicate a
pH, l·ieather vectors, rainfal
major ions, geol
Can. Tech. Rep. Fish.
dans 1 'eau de x lacs du sud lacs Mosquito, Robin et etait de 5 a 6,0.
on avec le ie local e.
a lle/1 et neutral ite.
denote
de la pl e, les
preservative v.rcLs added ..
on ice or refrigerated tmtil
buffers ..
in kept
I
-2-
morainic are two or three cottages and fishing camps on t.he
STEll\ lJ-<6,KE
southwestertl corner.
CkEASEY
developed in Devonian granireo
KERR
-4-
trends occur ..
other Clions
derived primarily from sources outside the prov
units~
increased loading~
i.e
the
in lr:lsh
Jef
of
-8-
Ls.ke
Robtn Hood
p
Year
Long.
67 65 °2 (J'
66°19 1
66°34'
10i.9
Nay 3-5
Chisholm (),.6
Distance
July
5 8<).
7-20
23.0
area (ha)
52 3000
38<J
area drainage area
8 67 91
5
44.8
---------------------
Sept. tor.al
102. .. 5
Table
Stein
Ju;lP
3-5 12-19
50 25
23*( 12 l 5 22 20
30
50
Aug~
9-17
n5 25 LD
20 22 35*
'' -' 35 42 65
Se Sept. S-7 22-27
55 60 58 23 25
')'-~J 18
20 20 19 25 22
14* 30 28
35 33 28* 40
55 60 57
Surfa e 's lakes surveyed for May-late September 978. Aster sks indicate values Which appear to be out of line with the major ty
3-5
the readings, are not lncluded in the mean ..
12-19
7" () 7. 1 5.9 5.6 5. 7.2*
.'j
7.2 7. 3*
Sept. 7-20 9-17 5-7
7. 5 8.n 7 ~ 7 7. 4* 6.8 6. 7
6.9 7.0 6.9 7.2 6.8
Se 22-27
6.9 7
7 .. l
(.
31
6.9
7.0
7. 7.
0 5.8
7 ;0 l \.Jhea ton 7. 4* 6.8 7.2 7.2 2 7.0 7.
- 1-
'i'abl.e
Lake iiJay June :uly
Creasey Kerr
7 illeasure
ments 'He.re made in al.l
90
sampling lOO
Table 6 B. Normal i ze.d
*
Stein \..Jheaton
>r1ean
the
• 84 • 86
• 82
59 70
88
34
76 99 85
21
104
o.
o.
Cl- for Values
July
l.2i(l. • 88
,Cl • 88
l. 04
• 97
Late Sept ~ Sept ,. Mean
80 qr) 107 86 90 107 87 99 98
106 128 105 .. 5
• 007
wo
various lakes with res pee t parentheses Chisholm Lake
Aug • Se
• 98) i•
l. l. o • l. 24
.95 l. 22
.01 L l. 20
' '.
'.Jct:::nn i.e sources are given are r.he of the two
2-
cs
normal values as explained tn Table
28(29)
R(J l;(ll) 4(92) !t0(77) 3(88) 26(70)
12 ( 79 54)
.42 .os
. 88 "98 l. Creasey • 90 9' • '-! .99 Kerr .93 • 98 L.
.88 ! . • 88 .99 • 99
.84 ! . ( • 91) • 9tl) (i.
----~-~-------·--
8. >lonthly potassium
Aug.
32(24)
28(89) !9(8)) 26(170)
' "/ i" 1-T
; • 09 i. ()1,
l. 02 1.07 1.00
!. 05 (l. 03)
Late Re pt.
--------------
41(8'J)
• 14 .09
l. 13
33 ( 32) 18(30)
2
O(l GO) 0(187)
l. 04 • 98 • 99 • 98
!. 04
• 97
• 99 (. 98)
) 72)
(l.leq surface water sarnples calculated to be derived from
oceanic sources are given i.n fJ.:1renthe.ses,. Totdl concer:trations ;ore the the two
Aug. Sept. Mean
:1tld 22(1) 20(0) 22(l) 22 (1) 7(1) ( ) 8(0) 9(1 8(1) 4 ( l) 3( 2) 6(2) 4(1) )
l) ) 1 )
4(1) 13(2) 9(2)
Stein 1(2) 2 ( 1) 3(2) ]I ) ' \ .._) 3(2) 4(4 3(5) 4(6) 4(5)
7(2. 4. i. 4(2. o. 6. .7) s.
Table 9.
L._1..ke
Creasey Kerr
11. Stein
for 7 lakes
La.ke
I.OD
Chisholm Robin Hood C·1o squi to Cre2sc y
i·ionlb ly for 7
June
77
1(7)*
July
69(1 (8 (2
28(6) 10(20)
sur face water samples derived from
trations
Sept.
59(6 96(10) 79(8) 77(lG) 94(: 0) 63(20)
88
pt.
) 30(4) 16(18)
:-lean
54(7) il7(9 7il(il)
Mean
cunr :\mounts calculated
sources are given in parenthe:;es .. CWO
•?:>rruneously low ..
196(4) 1 97 ( 8)
-~----------------·-~--·---------~---~----
}1uti Lt60 70 100
(J 32 64 <10 52 <10 58
i06 Stein 144 \•!he a ton 15!+ 118 iil9 138
77
Se
b4S(i) l
201(4) j 97
579 160
30
l Sb ( 4)
569(2) )
145(4) 1(4) 191
( l;})
the
be
surface of l..a ke is considered
zP.rv for averaging ..
5G8 l04
2.4 26
102 i63 150
Tabll'
Bul Lon
Chisholm
Kerr
Steir: Wheaton
Fixed end-
Kobln Hood 32 ~1osqui 30 Creasey Kerr
-15-
To :a l in flee tion I.abora tory determinations
40 <l ()
·-----------------· -----------
Neans 1'16 J'!
"'
entrations four heavy s ( ~eq unfiltered w-ater samples taken from the various lakes; nm = t measurable,.
t.
Pb++ Mn++
0 .. r.-lg 56 0.88
0 o. 0.85 0.85
L 53
003 o. nm o. 73 o.oos u. 57 o. 038 0.006 u. 77 0.002 l. 25
(),. 031-t rl!'T! 0 .. 003 0.59 o. 05 7 rr:n fl."TT 0.36 nm 0.009 0.26 o. 03J nm 004 o. 70 021 0.004 o. 86 nm !. 07
Lake cu++ Cd ++ Pb++ Mn++ pH
7. 0
Creasey (J.OJ"l i). 007 Kerr o. 02 3 lJI!l 0.003 0.69 6 .. 6
o. 03 003 o. 86 !.
o.
-lli-
probably due LO erroneously lo• . .;r HCOJ- dPtcn:Jinrttinn~
Mud Bo1 to'1 109* Chisholm -6 -ll
l\j
-34 2l, -5 ·-5
-22 23 24
-2) J.O -o 39
-9 54 21 -35
-2S -4
-2
Lh -2C
-3 -5
'30
l'J
the ten surveyed The lakes
: l. ~1ud;
Robin Hood; 5 .. Mosquito; 9. 'till; and
lakes and
plus measu~ements of cemperat11re, pH
tivity
drainage
i\r rry,vs - direction of water flow ..
-17-
Fig. 2
Fig. 3
• 4
t N
I
Mosquito
• 7
8
0 Q
Fig.
E
0
0 l-
John Airpori
l patterns through Nay-September) St. Biological Station and
Andrews as
Fig~ 16 ~ total ionic composition surface ~,..,rater samples (each point a sean for seven lakes) as
Increase in
_L ____ _l_ __ ~-
from Line
I_ cy L •
JL)
concentrations calculated to be vs .. is
Alk.a.linity titration curves each of :surveyed<!! were per formed in
the. pH
-24-
600
plot ted as TI1e ionic composition lakes surveyed, as derived from oceanic sources, from other sources, composition (sum of the previous two). are ordered that distance
coast as one progresses from left
Di trogen and -) concentrations ( in surface water samples the various lakes
Late Lake Sept 0
Hud 400 <!0 < <10 Bolton 150 <!0 <iO <!0 Chisholm 5(J <10 <10 <10 Robin <10 Mosquito Creasey Kerr Mill 1400 Stein <10 <10 20 10 Wheaton 50 <10 <10 <10
Phosphorus concentrations ( ~ g/L) surface samples from the various lakes.. * indicates not included in determinatton of means
Lake Msy Aug. Sept'
10 12 12 9 ll ll 4 8 li 16 74*
.) 2 2 2
Kerr 12 13
5 21 <l q h 0 ll
APPENDIX
concentrations (mg/L) surface water various lakes. Determinations were made on Se
flo l ton Chisholm
0.2 Creasey Kerr Mill Stein Wheaton
La Sept.
o. l l.l o,. l 1 .. 4 o. l. 5 1.2
• 6 1. 4 0 .. 2
Late Sept. Mean
10 7 8
11 3 3
2
5 !0
7 8
from the