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Czech J. Anim. Sci., 48, 2003 (11): 481486 Original Paper
481
Increased awareness of the inuence of diets onhuman health has prompted producers to producefood of higher quality, rich in nutrients and nu-traceuticals, in environmentally friendly manner.On the other hand, raw materials for food pro-duction are getting poor in essential minerals andvitamins at the same time.
Milk and dairy products have been recognizedall over the world for a long time as good for theirsensory properties, but also for their benecial in-
uence on human health (Steijns, 2001). On theother hand, milk is an expensive raw material pro-duced by animals (Boland et al., 2001). To producemilk or to make its products of good quality and toreduce their price, a good raw material is needed.erefore constant control of raw milk boughtfrom farms is necessary. Milk should be controllednot only for fat and proteins as it is usual, but alsofor mineral content wheneverpossible.
Milk is known as an excellent source of Ca, andit can supply moderate amounts of Mg, smaller
amounts of Zn and very small amounts of Feand Cu (Levyet al., 1985; Pennigton et al., 1987,
1995a,b). erefore the essential metals are inter-esting for determination of their adequate dailyintake by the organism. On the other hand, dueto the growing environmental pollution it is alsonecessary to determine and monitor the levels oftoxic metals in milk, such as lead and cadmium,because they can signicantly inuence the humanand animal health (Steijns, 2001).
e most frequently used technique to deter-mine metals in food and biological materials is
atomic absorption spectrophotometry (AAS). Ifthe concentrations of metals are high enough, AASdeterminations are usually done by ame atomicabsorption spectrophotometry (FA-AAS). Whenthe concentrations of metals are low, electrothermalatomic absorption spectrophotometry (EA-AAS) isapplied. Both techniques should give the sameresults if the concentration of metals is above thedetection limit of FA-AAS (Jorhem, 1993).
Because of low industrial production Croatia hasa unique opportunity to produce milk rich in nu-
tritional elements and with very low levels of toxicsubstances at the same time. In order to determine
Determination of metals in cows milk by ame
atomic absorption spectrophotometryM. SIKIRI1, N. BRAJENOVI1, I. PAVLOVI2, J. L. HAVRANEK2, N. PLAVLJANI2
1Ruer Bokovi Institute, Zagreb, Croatia2Faculty of Agriculture, University of Zagreb, Zagreb, Croatia
ABSTRACT: e essential (Ca, Cu, Fe, Mg, Mn, Zn) and toxic metals (Pb and Cd) were determined by ameatomic absorption spectrophotometry (FA-AAS) in raw cows milk. Milk was sampled four times in March 2000
on fteen farms near Kri in the Zagreb region from bulk milk directly into plastic bottles (to avoid contamina-
tion). e raw cows milk samples were digested in an MLS-1200 Mega Microwave Digestion System with MDRTechnology, and the metals were determined directly by FA-AAS in the solutions of digested samples. Statisticalanalyses were performed using statistical software SAS v. 8.0. Contents of essential minerals (Ca, Cu, Fe, Mg, Mn,
Zn) in milk from Croatian farms are on the normal levels in comparison with the data from other countries. elevel of toxic metals (Pb and Cd) was lower than the tolerance level dened by Croatian regulations (Pb < 100 g/l
and Cd < 10 g/l).
Keywords: lead; cadmium; copper; iron; manganese; magnesium; calcium; raw cows milk; ame atomic absorption
spectrophotometry
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Original Paper Czech J. Anim. Sci., 48, 2003 (11): 481486
the quality of raw material bought by the Croatiandairy industry one-month research was conductedon 15 family farms in the region of Ivanic grad, theregion of biggest milk producers in Croatia. Ourattention was focused on the mineral composition
of milk.
MATERIAL AND METHODS
Sampling strategy. Samples of raw cows milkwere collected four times in March 2000 fromfteen farms located near Kri in the Zagreb re-gion. e cows on each farm were fed dry hay andmineral premixes and drank water from the pump.Raw milk was sampled from the bulk milk of the
farms directly into carefully washed plastic bottlesbecause of the relatively great possibility of samplecontamination, especially by lead and cadmium.
Precautions against contamination. All chemi-cals were of the highest available purity. Deionised
water was used. e laboratory ware was cleanedwith chromosulphuric acid and rinsed with deion-ised water. e laboratory ware was dipped in10% HNO
3for 24 h, rinsed with deionised water,
dipped in 3% EDTA solution for 24 h and rinsedwith deionised water again.
Anakytical procedure. e fat and protein con-tent (%) was determined on Bently 150 Infraredmilk analyser.
To determine the concentrations of metalschemicals of the highest available purity wereused. HNO
3(Riedel) was used for the dilution
and mineralization of raw milk samples, H2O
2(9.791 mol/dm3, Riedel) was used for digestionof all milk samples. Lead nitrate (3.019 103mol/dm3, Merck) and cadmium nitrate (4.230 103 mol/dm3, Merck) solutions were used ascalibration standards. All solutions were prepared
with deionised water.e metals (calcium, copper, iron, magnesium,
manganese, zinc, lead and cadmium) were ana-lysed by FA-AAS in a total of 60 milk samples. Toeliminate the organic part of milk, 0.500 g of rawcows milk was treated with 6 ml of 65% HNO3and 1 ml 30% H
2O
2, mixed and digested in an
MLS-1200 Mega Microwave Digestion Systemwith MDR Technology. Lead and cadmium weredetermined with ammonium salts pyrrolidine-1-dithiocarboxylic acid (APDC) into methyl-isobutyl
ketone by FA-AAS. e other investigated metalswere determined directly by FA-AAS.
Instrumentation. PU 9100X FA-AAS equippedwith Epson FX-850 printer was used. e instru-ment was controlled by Philips P 3120 PC. e air/acetylene ame was used for the analysis of metals.Instrumental conditions for the determinations of
metals in raw cows milk are given in Table 1.Statistics. Data were analysed by General Linear
Models procedure. Mean dierences were sepa-rated by Duncans Multiple Range Test. e levelof signicance was set at P< 0.05. All analyses wereperformed using statistical software SAS v. 8.0.
RESULTS
Average mineral concentration of raw cows milk is
shown in Figure 1. e results of ANOVA are sum-marized in Table 2. Signicant correlations betweenthe investigated parameters are shown in Figure 2.
Fat and protein
In the period of investigations fat content in rawcows milk from 15 dierent farms was signicantlydierent, ranging from 2.55 to 4.62%. Similar re-sults were obtained for protein content that rangedfrom 2.81 to 4.1%. e correlation between fat andprotein content was not statistically signicant.
Calcium and magnesium
Dierences between farms were signicantfor calcium content, ranging from 1 125.76 to2 019.04 mg/kg, but not for magnesium content136.02196.67 mg/kg. Calcium content correlated
with fat content (R= 0.647).
Iron, zinc, copper and manganese
Iron, zinc, copper and manganese contents inmilk from dierent farms were statistically dif-ferent. Relatively high coecients of correlationof manganese and copper with the other threeminerals were obtained (Mn Fe: R= 0.641, Mn Zn: R= 0.731, Mn Cu: R= 0.618, Cu Fe:R= 0.613, Cu Zn: R= 0.629) while the contentsof iron and zinc were not so highly correlated. In
addition, correlations existed between copper andcalcium content (R = 0.629) as well as between
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Czech J. Anim. Sci., 48, 2003 (11): 481486 Original Paper
483
Table1.Instrumentalconditionsforlead
,cadmium,calcium,copper,iron,m
anganese,magnesiumandzincdeterminationinrawcowsmilkbyFA-AAS
Lead
Cadmium
Calcium
Copper
Iron
Manganese
Magnesium
Zinc
Prim
arywavelength(nm)
217.0
228.8
422.7
324.8
248.3
279.5
285.2
213.9
Band
-pass(nm)
0.5
0.5
0.5
0.5
0.2
0.5
0.5
0.5
Injec
tionvolume(ml)
1
1
1
1
1
1
1
1
Flam
etype
air/acetylene
Fuel
owrate(l/min)
0.91.2
1.01.3
0.91.2
0.81.1
0.81.0
0.91.2
0.91.2
0.91.2
Sensitivity(mg/l)
0.10
0.032
0.09
0.041
0.060
0.029
0.003
0.013
Table2.ANOVAsummaryofthefarme
ectonminerallevelsinrawcowsmilk.Meanswiththesameletterare
notsignicantlydierent
Protein
Fat
Ca
Mg
Fe
Zn
Cu
Mn
Pb
Cd
(%)
P
Mn. is sequence is similar tothat obtained by Rodrguez et al. (1999), the onlydierence being the sequence of Cu and Fe.
It is known that the metal concentration in milkcan vary due the factors inuencing its secretionfrom the mammary gland, such as breed of the ani-mal, season of the year, feeding and factors related
Table 3. Average mineral composition of raw cows milk from dierent countries
Country Ca (mg/kg) Mg (mg/kg) Fe (mg/kg) Cu (mg/kg) Zn (mg/kg) References
Italy 0.65 0.21 3.82 Del Petere, DiStanislao (1984)
Spain 1 251 48 116 3 0.46 0.10 0.16 0.02 3.70 0.22 Zuerera-Cosanoet al. (1994)
Pakistan 0.60 0.45 4.20 Bano et al.(1985)
Croatia 1 403.94 322.33 165.01 37.97 0.13 0.02 0.38 0.12 0.51 0.16 this paper
Figure 1. Composition of raw cows milk from dierent farms: a) protein and fat; b) Ca and Mg; c) Fe, Zn, Cuand Mn; d) Pb and Cd
I II III IV V VI VIIVIIIIX X XI XIIXIIIXIVXV0
1
2
3
4
5
6
(%)
Farm
Protein
Fat
I II III IV V VI VIIVIIIIX X XI XIIXIIIXIVXV0
500
1000
1500
2000
(mg/kg)
Farm
Ca
Mg
I II III IV V VI VIIVIIIIX X XI XIIXIIIXIVXV0.0
0.2
0.4
0.6
0.8
(mg/kg)
Farm
Fe
Zn
Cu
Mn
I II III IV V VI VIIVIIIIX X XI XIIXIIIXIVXV0
20
40
60
(g/kg)
Farm
Pb
Cd
c) d)
a) b)
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Czech J. Anim. Sci., 48, 2003 (11): 481486 Original Paper
485
to animal handling by humans (Moreno-Rojas etal., 1993; Zurera-Cosano et al., 1994). In this studythe animals on the farms were of the same breed,samples were taken in a relatively short period, cows
were fed the same concentrate but dierent dry hay.erefore the statistically signicant dierences inthe content of essential minerals between the farmscan be ascribed to dierent dry hays. Lead and cad-mium are toxic minerals often associated with trac
pollution, therefore variations of their levels in milkfrom dierent farms are likely due to the locationof meadows in relation to roads. Tolerance limitsofthese two toxic metals according to Croatian legis-lation are: Pb < 100 g/l, Cd < 10 g/l (NarodneNovine, 1994). Lead and cadmium levels in milkfrom all investigated farms were below these limits.
In comparison with the average mineral composi-tion of raw milk obtained by investigations in Italy(Del Petre and Di Stanislao, 1984), Spain (Zuerera-Cosano et al., 1994) and Pakistan (Bano et al.,
1985), milk from Croatian farms has more Ca andMg, similar content of Cu and lower content of Fe
2.6 2.8 3.0 3.2 3.4 3.6 3.8 4.0 4.2 4.4
0.00
0.02
0.04
0.06
0.2
0.4
0.6
0.8
1.0Zn
Cu
Mn
0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
0.0
0.2
0.4
0.6
0.8
1.0
1000
1500
2000
2500Ca
Fe
Zn
Figure 2. Correlations between: a) Zn, Cu, Mn and protein; b) Ca and fat; c) Ca, Fe, Zn and Cu; d) Fe, Zn, Cuand Mn in raw cows milk from dierent farms
1 2 3 4 5 6 7
0
500
1000
1500
2000
2500 Ca
0.02 0.03 0.04 0.05 0.06 0.07
0.0
0.2
0.4
0.6
0.8
1.0 Fe
Zn
Cu
and Zn (Table 3). However, it should be noted thatdeviations are much larger in our investigation.
Relatively low correlation coecients are in ac-cordance with previous studies (Rodrguez et al.,1999). is was explained by the relatively narrowrange of metal concentrations found in certaintypes of milk.
CONCLUSIONS
Contents of essential minerals (Ca, Mg, Fe, Zn.Cu, Mn) in milk from Croatian farms are on thenormal levels in comparison with the data fromother countries. e statistically signicant dif-ference in their contents in milk obtained fromdierent farms implies the necessity of control-ling mineral levels in milk by the dairy industry.Lead and cadmium levels in milk from all inves-tigated farms are below the limits as dened by
the Croatian legislation, indicating a possibility ofproducing organic products.
Protein (%) Fat (%)
Cu (mg/kg) Mn (mg/kg)
(m
g/kg)
(mg/kg)
(m
g/kg)
(mg/k
g)
a) b)
c) d)
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Original Paper Czech J. Anim. Sci., 48, 2003 (11): 481486
REFERENCES
Bano N., Naeem M., Khan H.H. (1985): Trace metal
studies in milk, milk products and eggs. J. Nat. Sci.Math.,25, 6774.
Boland M., MacGibbon A., Hill J. (2001): Designermilks for the newmillennium. Livest. Prod. Sci., 72,
99109.Del Petere V., Di Stanislao F. (1984): Trace elements in
cow milk sold in Marche Region. Nuovi Ann. Ig.Microbiol.,35, 313323.
Jorhem L. (1993): Determination of metals foodstusby atomic absorption spectrophotometry after dry
ashing: NMKL1 interlaboratory study of lead cad-mium, zinc, copper, iron, chromium, and nickel. J.
AOAC Inter., 76, 798813.
Levy Y., Zeharoa A., Grunebaum M., Nitzan M., Stein-herz R. (1985): Copper deciency in infants fed cowmilk. J. Pediatr., 106, 786788.
Moreno-Rojas R., Zurera-Cosano G., Amaro-Lpez M.(1993): Micronutrients in natural cow, ewe and goat
milk. Int. J. Food Sci. Nutr., 44, 3746.Narodne Novine (1994): Regulation of allowed pesti-
cides, toxins, mycotoxins, metals and histamine andsimilar substances in food. 46, 1583.
Pennigton J.A.T., Wilson D.B., Young B., Johnson R.D.,
Vanderveen J.E. (1987): Mineral content of marketsamples of uid whole milk. J. Am. Diet. Assoc., 87,
10361042.Pennigton J.A.T., Schoen S.A, Salmon G.D., Young B.,
Johnson R.D., Marts R.W.J.E. (1995a): Compositionof core foods of the U.S. Food Supply, 19821991.II. Calcium, magnesium, iron and zinc. J. Food
Comp. Analysis, 8, 129169.Pennigton J.A.T., Schoen S.A., Salmon G.D., Young B.,
Johnson R.D., Marts R.W.J.E. (1995b): Compositionof core foods of the U.S. Food Supply, 19821991.
III. Copper, manganese, selenium and iodine. J. FoodComp. Analysis, 8,171217.
Rodrguez E.M., Sanz Alaejos M., Diaz Romero C.(1999): Chemometric studies of several minerals in
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Received: 030121
Accepted after corrections:031015
ABSTRAKT
Stanoven obsahu kov v kravskm mlce pomoc plamenov atomov absorpn spektrofometrie
Obsahy zkladnch kov (Ca, Cu, Fe, Mg, Mn, Zn) a toxickch kov (Pb a Cd) v syrovm kravskm mlce bylystanoveny plamenovou atomovou absorpn spektrofotometri (FA-AAS). Vzorky mlka byly odebrny tyikrt
v beznu v roce 2000 na 15 farmch pobl Krie v zhebsk oblasti ze smsnho mlka pmo do plastovch lahv(aby se pedelo kontaminaci). Vzorky syrovho kravskho mlka byly podrobeny mineralizaci v mikrovlnnm
digesnm systmu MLS-1200 Mega pomoc technologie MDR; obsahy kov byly stanoveny pmo pomoc FA-AASv roztocch vzork, kter proly mineralizac. Ke statistickm analzm byl pouit statistick software SAS v. 8.0.
Obsahy zkladnch kov (Ca, Cu, Fe, Mg, Zn) v mlce z chorvatskch farem jsou ve srovnn s daji z ostatnch
zem na normln hladin. Hladina toxickch kov (Pb a Cd) byla ni ne povolen limity, kter denuj chor-vatsk pedpisy (Pb < 100 g/l a Cd < 10 g/l).
Klov slova: olovo; kadmium; m; elezo; mangan; hok; vpnk; syrov kravsk mlko; plamenov atomovabsorpn spektrofotometrie
Corresponding Author
Dr. Nataa Brajenovi, Ruer Bokovi Institute, P.O.Box 180, 10002 Zagreb, Croatia
Tel. +385 1 468 01 25, fax+385 1 468 02 45, e-mail: [email protected]