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Six measurements of PCDD/PCDF and five measurements of brain function with Single Photon Emission Computed Tomography (SPECT) in one individual. A case-study.

Karl-Rainer Fabig,

Practitioner, Immenhoeven 19, D-22417 Hamburg

Abstract

Six repeated measurements of PCDD/F in blood lipids and five repeated semiquantitative measurements of the regional cerebral blood flow (rCBF) with SPECT (99m Tc-HMPAO) between 1990 and 1997 in one individual with moderate exposure to PCDD/F lead to three conclusions:

  1. There is no influence of ageing on PCDD/F in this subject.
  2. Loss of lipids and body mass index elevate the body burden of PCDD/F.
  3. The reduction of the rCBF is related to the body burden of the most toxic congeners of PCDD/F.

Introduction

PCDD/F concentrations have been analyzed in exposed and unexposed populations. The background body burden and increased internal doses can be distinguished. Data show an age-dependency of the PCDD/F-body burden 1) and a secular trend toward lower internal doses. 2,3)

The patient was born 1927 in Hamburg and emigrated to the USA. He operated a special wood factory in Pennsylvania from 1950 to 1990. In 1973 the factory buildings were treated with wood preservatives like pentachlorophenol, which were imported from Germany. The patient sought medical help in Germany. After recognizing the problem first step was to stop exposure in 1990. In Jan. 1991 PCP in his serum was 8.0 µg/l.

The wife of the patient was born 1920 in the USA. She never had any exposure to PCDD/F. Therefore she was taken as background control with two measurements of PCDD/F. The exposed husband became ill in the years before 1990. Colitis and other diseases arrise. The most symtpoms were neuropsychological like vertigo, cephalgia, loss of concentration, energy and spontanous doing, neurasthenia. The highest stage of these symptoms were in 1993 to 1994, after loss of weight due to a serious infection, which was not caused from PCDD/F.

The objectives of these symptoms were analyzed with SPECT of brain.

This case study was driven by two hypotheses:

1. PCDD/F are stored in adipose tissue, and would be liberated into serum, and thus increase in concentration, upon weight loss.

2. CYP1A1 is known to be induced by PCDD/PCDF and found in the pyramidal cells of the neopallium and in the neurones of the central thalamic nuclei of the rat 4) . There may be similar conditions in humans. Then different body burden with TCDD (and other congeners) would result to different findings in measurements of brain function with SPECT.

Methods

PCDD/F in blood lipid of the exposed man were analyzed six times, PCDD/F of the unexposed woman were analyzed two times since 1990. Blood samples were determined by the ERGO Company, Hamburg. Dioxins were extracted from 40 to 60 g samples of whole blood and measured by gas chromatography/mass spectroscopy 5) . The findings are expressed in pg/g extractable lipids, i.e., part-per-trillion (ppt) concentration on lipid basis. The sum of PCDD/F is expressed as International TEQ 6). Lipid concentration was determined as the sum of cholesterol and triglycerides. The body-mass index was defined as the body weight in kg divided by the height*height in m².

The regional cerebral blood flow (rCBF) of the exposed man was analyzed five times since 1990. The Nuclear-Radiologist Dr. E.-U.Bieler, Hamburg, performed the Single Photon Emission Computed Tomographies. Tracer of these SPECT was the high lipophilic substance 99m-Tc-HMPAO 7,8). The measurements in this SPECT follow the otherwise described method of "region of interest"(ROI) 9) . The regional cerebral blood flow ist expressed in percent (semiquantative). A reduction of rCBF ³ 10 percent in a cortex area of 3 x 3 cm around is commonly a sign of disease. 

ORGANOHALOGEN COMPOUNDS

Vol. 37 (1998) 23

Results and Discussion

Changes in PCDD/F concentration, body mass index and lipids of the exposed man and changes in PCDD/F of the unexposed women, which is seven years older then he, are shown in table 1.

Table 1

PCDD/F concentration of control and the exposed individual (with body mass index and lipids)

exposure

date of

Age

ITEQ 2,3,7,8-Tetra- 1,2,3,7,8-Penta- BMI Cholesterol +

sample

(pg/g) CDD (pg/g) CDD (pg/g) (kg/m²) Trigl. (mg/dl)
PCDD/F

10.09.90

63.1

34.3

4.9

9.7

26.00

405

background

01.11.91

71.3

20.9

5.7

6.5

PCDD/F

13.10.92

65.2

29.7

4.6

9.0

24.84

410

PCDD/F

12.06.94

66.9

56.2

6.9

17.2

19.98

291

background

02.03.95

74.6

18.0

2.9

6.1

PCDD/F

16.04.95

67.7

30.1

4.2

9.8

23.33

415

PCDD/F

02.04.96

68.7

32.5

4.6

10.6

21.86

380

PCDD/F

22.04.97

69.7

29.6

4.8

10.0

22.15

308

 

ITEQ of exposed was found significant higher than ITEQ of unexposed (Mann-Whitney test, p < 0,02).

A reduction in the body burden in both over calendar time could not be detected (figure 1).

Figure 1

Calendar year and ITEQ between 1990 and 1997

 

Figure 1 did not indicate an increasing level of ITEQ in ageing of both exposed or not exposed.

However figure 2 shows that reduction in body mass index (also in the sum of cholesterol and triglycerides) of about 25 % in the exposed man is related to an increase in ITEQ of 90 %. The secular trend might be masked by the change of lipid concentration in 1994.

ORGANOHALOGEN COMPOUNDS

Vol. 37 (1998) 24 

Figure 2

I-TEQ (NATO/CCMS) and body mass index

Excluding the one increased concentration, then PCDD/F plotted over the body mass index (figure 2) does not show a diluting effect as supposed by Pless et al. 1993 10). A loss of weight seems to be associated with redistribution of PCDD/F and a higher lipid concentration. A moderate exposed person can during his life be exposed to higher concentration when loosing weight. The increase can also trigger the development of new and the worsening of existing symptoms. Backward estimation of PCDD/F is applied to calculate the potential risk of disease for past exposures 11). It is often assumed a one compartment model and a long elimination half-life of most of the 2,3,7,8-substituted PCDD/F congeners. Factors associated with lipid mobilisation may modify the body burden. The data suggest a need to take changes in body fat along with other indices of exposure into account when attempting to determine past exposures as risk factors for disorders/diseases.

Table 2 lists age at sample, age at SPECT and reduced rCBF (in prefrontal and premotoric regions of brain). The SPECT findings in 1993 (age 66,2) include the opercula fronto-parietale and fronto-temporale. The most significant reduction of rCBF was 24 percent.

Table 2

Age at sample, age at SPECT and reduction of rCBF

age at sample

age at SPECT brain

Reduced rCBF

65.2

63.8

8%

66.9

66.2

24%

67.7

67.3

14%

68.7

68.7

15%

69.7

69.8

13%

Ageing is often an important confounder of physiological or medical findings. A reduction of rCBF in SPECT is seen in pathological ageing.

However reduction of rCBF in relationship of ageing is not seen in figure 3.

ORGANOHALOGEN COMPOUNDS

Vol. 37 (1998) 25

 

Figure 3

Reduction of rCBF and age

The both most toxic PCDD/F-Isomers were plotted against rCBF (figure 4 and figure 5).

 

Figure 4

Reduction of rCBF and 2,3,7,8-Tetra-CDD

 

 

Linear regression gives the following equation:

- rCBF = -8.0 + 4.6 *(2,3,7,8-Tetra-CDD) (R= 0.85).

 

ORGANOHALOGEN COMPOUNDS

Vol. 37 (1998) 26

 

Figure 5

Reduction of rCBF and 1,2,3,7,8-Penta-CDD

Linear regression gives the following equation:

-rCBF = -3.8 + 1.6 *(1,2,3,7,8-Penta-CDD) (R=0.94)

The neuropsychological symptoms were most seriously at the age of 66, when reduction of rCBF was the highest. The symptoms of toxic encephalopathia 12) increased in time of the highest levels of 2,3,7,8-Tetra-CDD and 1,2,3,7,8-Penta-CDD. In 1993 Zober and Paepke13) published levels of 2,3,7,8-Tetra-CDD in premortal blood and in postmortal brain of three workers from BASF company . Case 3 in table 3 is a worker, who lost extremely body mass before he died. The loss of weight caused a higher level of 2,3,7,8-TCDD in blood lipid (7482 pg/g). 25 percent of this concentration in blood was concentrated in brain.

 

Table 3

2,3,7,8-Tetra-CDD in blood lipid and in brain (pg/g) of three BASF workers 13)

case

2,3,7,8-TCDD blood

2,3,7,8-TCDD brain

ratio brain/blood

1

255

36

0.14

2

32

7

0.22

3

7482

2457

0.33

 

After loosing weight weight PCDD/F from adipose tissue will be found in blood lipids.12-15 percent of this blood enter normally the blood-brain barrier (BBB ) via arterial blood flow. High lipophilic molecules like 2,3,7,8-Tetra-CDD and 1,2,3,7,8-Penta-CDD (molecular weight smaller than 400 Dalton) are perfectly able to diffuse through the "tight epithelium"14) of BBB into neurones 15) .

 

The high toxic 2,3,7,8-Tetra-CDD and 1,2,3,7,8-Penta-CDD are causing pathological SPECT brain findings in this not extremely exposed subject.

These congeners seem to be permeable through the blood-brain barrier in vivo. They may induce the CYP1A1 existing in some brain compartments.

 

ORGANOHALOGEN COMPOUNDS

Vol. 37 (1998) 27

  

Literature Cited

(1) Schrey P.; Wittsiepe J.; Ewers U.; Exner M.; Selenka F. Age-related increase of PCDD/F-levels in human blood - a study with unexposed persons from Germany. Organohalogen Compounds 1992, 9 261-267.

(2) Paepke O.; Ball M.; Lis Z.A.; Wuthe J. PCDD/PCDFs in humans, follow-up of background data for Germany  Chemosphere 32, 1996, 575-582.

(3) Spannhake K.; v.Manikowsky S.; Paepke O.; Zier B.; Fabig K.R.; Karmaus W.; Osius N.; Neus H.; Schuemann M. Finding appropriate reference data for formerly PCDD/PCDF-exposed female teachers. Organohalogen Compounds 1996, 30, 172-175.

(4) Kapitulnik J.; Gelboin H.V.; Guengerich F.P.; Jacobowitz D.M. Immunohistochemical localisation of cytochrome P-450 in rat brain. Neuroscience 1987, 20, 829-833.

(5) Paepke O.; Ball M.; Lis Z.A.; Scheunert K. PCDD/PCDF in whole blood samples of unexposed persons. Chemosphere 1989, 19 1101-1108.

(6) North Atlantic Treaty Organisation, Committee on the  Challenges of Modern Society, editors.  International toxicity equivalency factor (I-TEF) method of risk assessment for complex mixtures of dioxins and related compounds. Report Number 177.

(7) Costa D.C.; Ell P.J.; Cullum I.D.; Jarrit P.H. The in vivo Distribution of 99Tc H-HM-PAO in Normal Man.  Nucl med Comm 1986, 647-658.

(8) Neirinckx R.D.; Canning L.R.; Piper I.M.; et al. Technetium-99m d,l-HM-PAO: a New Radiopharmaceutical for  SPECT Imaging of Regional Cerebral Blood Perfusion.  Nucl Med 1987, 28, 191-202.

(9) Podreka I.; Suess G.; Goldenberg M., Steiner T.; et al.  Initial Experience with Technetium 99m HM-PAO Brain SPECT. J Nucl Med 1987, 28, 1657-1666.

(10) Pless T.; Schneider F.; Steiner M.; Karmaus W. Impact of body-mass-index and age on the blood-concentration  of PCDD/PCDF of adults and children. Chemosphere 1993, 26, 1109-1118.

(11) Flesch-Janys D.; Berger J.; Gurn P. et al. Exposure to polychlorinated dioxins and furans (PCDD/F) and mortality  in a cohort of workers from a herbicide-producing plant in Hamburg, Federal Republic of Germany. Am J Epidemiol 1995, 142, 1165-1175.

(12) Cranmer J.M.; Goldberg L. Proceedings of the Workshop on Neurobehavioral Effects of Solvents.  Neuro Toxicology 1986, 7, 9-80.

(13) Zober A.; Paepke O. Concentration of PCDDs and PCDFs in Human Tissue 36 Years after  Accidental Dioxin Exposure. Chemosphere 1993, 27, 413-418.

(14) Crone C. The blood-brain barrier: A modified tight epithelium. In: A.J. Suckling; M.G. Rumsby; M.W.B. Bradbury (ed.) The Blood-Brain Barrier in Health and Disease. Ellis Horwood Ltd, Chichester, 1986.

(15) Levin V.A. Relationship of Octanol/Water Partition Coefficient and Molecular Weight  to Rat Brain Capillary Permeability. J Med Chem 1980, 23, 682-684.

 

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