This chapter of the report presents research data on the production of biogenic amines by fish species that are likely to be cold-smoked. Factors that affect the production of biogenic amines, particularly histamine, are discussed. The effect of the cold-smoking process on biogenic amine production or growth of biogenic amine-producing microorganisms is also assessed. Finally, areas requiring research to adequately determine the hazard of biogenic production in cold-smoked fish and fishery products are listed.
Cadaverine, putrescine, and histamine are diamines that may be produced post mortem from the decarboxylation of specific free amino acids (Table IV-1) in fish or shellfish tissue (Silla Santos 1996). The decarboxylation process can proceed through two biochemical pathways: endogenous decarboxylase enzymes naturally occurring in fish or shellfish tissue or exogenous enzymes released by the various microorganisms associated with the seafood product. Endogenous production of diamines is insignificant when compared to the exogenous pathway (Wendakoon and Sakaguchi 1992a). The nature of the microflora and the composition of the product affect the amount of decarboxylase a bacterial cell may release (Wendakoon and Sakaguchi 1992b; Suzuki and others 1990). In general, histamine, putrescine, cadaverine, tyramine, tryptamine, β-phenylethylamine, spermine, and spermidine are considered the most important biogenic amines in foods (Shalaby 1996). However, β-phenylethylamine, spermine, and spermidine are not end products of bacterial decomposition in fishery products.
|3 - aromatic amine |
1 - heterocyclic amine
2 - alipathic amine
Fish muscle is naturally rich in free amino acids and the content may increase even further post mortem. The high content of proteolytic enzymes in the intestinal tract is responsible for the rapid autolytic process (Gilberg 1978; Aksnes 1988) and the high free amino acid content in fishery products. Amino acid formation depends on the harvesting season and feeding activity prior to capture. For example, fish harvested in summer or feeding season quickly liberated large quantities of lysine and arginine (Aksnes and Brekken 1988).
The activity of amino acid decarboxylase depends on a range of factors, including fermentable sugars, pH, and redox potential (Gale 1946). The influence of environmental temperature, nature of microflora, decarboxylase activity, and intestinal tract content on biogenic amine formation may be major reasons for the discrepancies that have been reported in the literature concerning levels of biogenic amines in fresh and processed fish. Another reason for discrepancies may be poor experimental design. Regardless of the discrepancies, it is clear that a high amino acid content and bacterial activity could rapidly result in an elevated concentration of biogenic amines if the proper controls are not in place.
1.1. Safety aspects
Biogenic amines, particularly histamine, have been implicated as the causative agent in a number of scombroid food poisonings. There is individual susceptibility to biogenic amines. Clinical signs are more severe in people taking medications that inhibit enzymes that normally detoxify histamine in the intestine. Histamine exerts its effects by binding to receptors on cellular membranes in the respiratory, cardiovascular, gastrointestinal, and haematological/immunological systems and the skin. The symptoms of histamine poisoning generally resemble the symptoms encountered with IgE-mediated food allergies (Taylor and others 1989) and usually appear shortly after the food is ingested with a duration of up to 24 h. Symptoms may be gastrointestinal (nausea, vomiting, diarrhea), circulatory (hypotension), cutaneous (rash, urticaria, edema, localized inflammation), and neurological (headache, palpitations, tingling, flushing or burning, itching). Antihistamines can be used effectively to treat the symptoms. Despite all uncertainties reported, histamine levels above 500 - 1,000 mg / kg (500 - 1,000 ppm) are considered potentially dangerous to human health based on the concentrations found in food products involved in histamine poisoning (Ten Brink and others 1990). Even less is known about the toxic dose of other amines. Threshold values of 100 - 800 mg / kg (100 - 800 ppm) for tyramine and 30 mg / kg (30 ppm) for phenylethylamine have been reported (Ten Brink and others 1990). In estimating the toxic levels of biogenic amines, one should consider the amount of food consumed, the presence of other amines in the food or other dietary components, and the use of alcohol and medicine. An additional concern, especially if nitrite were to be used in cold-smoked products, is that secondary amines such as putrescine and cadaverine can react with nitrite to form carcinogens (Hildrum and others 1976; Taylor 1986; Ten Brink and others 1990; and Veciana-Nogues and others 1997).
Fish often associated with histamine poisoning are the scombroid fish belonging to the families Scomberesocidae and Scombridae. Fish included in these families are the tunas, bonito, mackerels, bluefish, and saury. Tuna and mackerel are the most common fish associated with the poisoning, but other fish are also associated with outbreaks of scombroid poisoning. Examples include mahimahi, sardines, anchovies, herrings, and marlin. The association of type of fish and biogenic amine poisoning may reflect the amount of consumption of a specific fish.
Research on the quantitative determination of histamine, cadaverine and putrescine in fishery products at FDA have resulted in the 2 only accepted Association of Official Analytical Chemists (AOAC) methods for regulatory purposes (Rogers and Staruszkiewicz 1997). The research was the basis for the establishment of the defect action levels used in FDA's regulatory programs. Recently, the Food and Drug Administration (FDA) (21CFR123) established a guidance level for histamine of 5 mg / 100 g (50 ppm) for assuring the safe consumption of scombroid or scombroid-like fish and recommended the use of other data to judge fish freshness, such as the presence of other biogenic amines associated with fish decomposition (FDA 1996). A maximum average histamine content of 10 mg / 100 g (100 ppm) has been established in the European Community (EC) for acceptance of tuna and other fish belonging to the Scombridae and Scomberesocidae families (Veciana-Nogues and others 1997). The EC has suggested that in the future a maximum of 300 ppm for total biogenic amines in fish and fish products may be an appropriate legal limit. It is important to note, however, that there may be a type of poisoning that does not arise from high levels of histamine. Thus a low histamine level may not be absolute assurance of a safe product. It may be more appropriate to say that the absence of decomposition in the fish renders it a safe product. As such, a safe product would have no evidence of spoilage including odors of decomposition, high histamine levels, and other amines such as cadaverine.
2.1. Histamine toxicity
Douglas (1970) reported that very large amounts of histamine could be given orally without causing adverse effects. He attributed this to the conversion of histamine to inactive N-acetylhistamine by intestinal microflora. Human subjects given up to 67.5 mg histamine orally did not produce any subjective or objective symptoms of histamine poisoning (Granerus 1968). Sjaastad (1966), however, administered 36 mg or more of histamine to subjects who subsequently developed symptoms associated with histamine toxicity. Symptoms appeared also with tuna sandwiches containing 100, 150, and 180 mg doses of histamine. Generally, high histamine levels are able to cause a toxic response, but subsequent research has indicated that other factors may also be responsible. When Clifford and others (1989) fed portions of spoiled mackerel containing 300 mg histamine and mackerel associated with an incident diagnosed as scombrotoxicosis to volunteers, there were no significant observable effects. A second study by Clifford and others (1991) was conducted on mackerel fillets associated with an outbreak of scombrotoxicosis. Statistical analysis failed to detect any differences in amine content between fillets shown to be scombrotoxic and those failing to induce nausea, vomiting, or diarrhea, and also failed to establish any significant relationships between the amine doses. It was concluded that no relationship exists between the concentrations of six amines (including histamine, cadaverine, and putrescine) and the onset of scombrotoxic symptoms. Ienistea (1973) reported the deleterious effects in relation to the amount of histamine ingested at one meal as follows:
|Mild poisoning||8-40 mg histamine|
|Disorders of moderate intensity||70-1,000 mg histamine|
|Severe incidents||1,500-4,000 mg histamine|
The role of saurine (implicated in histamine poisonings in Japan) as a compound able to act synergistically with histamine was reviewed by Arnold and Brown (1978), but it was later concluded that the compound was in fact histamine.
2.2 Toxicity potentiators
Histamine appears not to be the sole factor in causing toxicity since cases have also been observed from low contents of histamine (Arnold and Brown 1978; Murray and others 1982; Taylor 1986; Clifford and others 1989; Soares and Gloria 1994). Strong evidence exists that biogenic amines such as putrescine, cadaverine, spermine, and spermidine in fish tissue can potentiate the toxic effect of histamine by inhibiting intestinal histamine-metabolizing enzymes such as diamine oxidase (Hungerford and Arefyev 1992), potentiating histamine uptake, and liberating endogenous histamine in intestinal fluids (Chu and Bjeldanes 1981; Hui and Taylor 1983; Ibe and others 1991; Halasz and others 1994). It has been reported that fish implicated in a scombroid poisoning incident had high levels of inhibitors that interfere with histamine metabolism. Monoamineoxidase inhibitor drugs used for the treatment of depression, hypertension, and tuberculosis have also been observed to potentiate the toxic effect of histamine (Maga 1978; Taylor 1986).
Studies have shown that the levels of cadaverine in toxic or decomposed fish are generally several times greater than the levels of putrescine. When cadaverine was administered through stomach catheters simultaneously with histamine, peroral toxicity was observed in the guinea pigs (Bjeldanes and others 1978). Klausen and Lund (1986) reported that at 10 °C the high cadaverine contents of mackerel in comparison with herring could be responsible for mackerel often being implicated in scombroid poisoning and not herring, since histamine levels were similar in both. Cadaverine and putrescine, as well as other diamines, have been suggested to facilitate the transport of histamine through the intestinal wall and to increase its toxicity (Fernandez-Salguero and Mackie 1987b).
Arnold and Brown (1978) reported on the possibility that bacterial endotoxins, which are widespread, could result in hypersensitivity to histamine. These compounds are complex, heat-stable, lipopolysaccharide materials produced primarily by gram-negative bacteria. They also reported that endotoxin is known to be capable of inducing histamine release in animals (sometimes called endotoxin shock) similar to that seen in anaphylaxis. J. Baronowski (personal communication), however, reported extremely low levels of endotoxin in both good tuna and tuna known to have caused illness in humans.
From these discussions, it is clear that concentration of biogenic amines producing observable toxicity may differ significantly, depending on a variety of circumstances. Also, although a variety of histamine potentiators are known, there is not a clear understanding of the level and the manner by which synergism occurs.
3. Prevalence in fish
The prevalence of biogenic amines in fish depends on several factors that are described in this section. In general, concentrations in newly caught fish are low. Mietz and Karmas (1978) found that cadaverine values ranged from 1.16 - 10.36 ppm in high quality rockfish, salmon steaks, and shrimp. Also, putrescine levels ranged from 1.36 - 6.30 ppm in high quality lobster tails, salmon steaks, and shrimp. A prior study by the investigators (Mietz and Karmas 1977) reported that high quality tuna had cadaverine and putrescine values ranging from 0.24 - 5.32 and 0 - 1.84 ppm, respectively. There has been some concern regarding the accuracy of the analytical methods used in these studies. Gloria and others (1999) determined biogenic amines in 102 samples of albacore tuna (Thunnus alalunga) harvested off the U.S. Northwest from 1994 to 1996. There were significant differences of amine levels in fish from different years. Total levels of the six amines detected (spermine, spermidine, putrescine, cadaverine, histamine, and tyramine) varied from 0.59 to 4.65 mg/100g (5.9 to 56.5 ppm). These levels were probably lower due to the fact that the samples were frozen on board or chilled on board and immediately frozen after reaching the dock and kept at -40 °C (-40 °F) until analysis. Spermine was present at higher levels, followed by spermidine, histamine, putrescine, cadaverine, and tyramine.
3.1 Muscle type
In the study by Gloria and others (1999), no difference was observed on amine levels of upper and lower loin light muscles, but dark muscles contained higher spermidine (Table IV-2). Intestine wall samples contained high amine levels.
|Biogenic amines1 (ppm)|
|light muscle upper loin||0.68b (0.12)||0.26c (0.07)||0.00b||0.22ab (0.07)||0.13b (0.02)||0.00b||1.29c (0.17)|
|lower loin||1.21b (0.26)||0.25c (0.05)||0.00b||0.14b (0.05)||0.11b (0.06)||0.00b||1.77c (0.37)|
|dark muscle||2.50ab (0.97)||0.79b (0.18)||0.00b||0.06b (0.03)||0.07b (0.05)||0.00b||3.42b (0.72)|
|intestine wall|| |
|3.63a (1.18)||0.52a (0.25)||0.43a (0.16)||1.96a (0.59)||4.38a (1.33)||16.3a (4.59|
|1 Mean values (standard deviation) were calculated by using 0 for not detected levels (spermine -SPM, spermidine-SPD, histamine-HIM, putrescine-PUT, cadaverine-CAD æ 0.08; and serotonin-SER æ 0.18 mg/100g). Mean values with the same superscript in the same column do not differ significantly (p ≤ 0.05), Turkey test).|
Takagi and others (1969) examined the amounts of histidine and histamine in 21 aquatic species during spoilage. Their conclusions were consistent with those of other researchers in that more histamine was produced in the red muscle fish such as tuna and mackerel than in white muscle species such as rockfish. Within a given fish species, more histidine and histamine were found in white than in red muscle.
Wendakoon and others (1990) reported that most of the bacteria that convert amino acids into non-volatile amines possess more than one decarboxylase. In contrast to results reported by Wendakoon and Sakaguchi (1992b), they also reported that in the dark muscle, the amine levels were always much higher and the amine production was more rapid than that in the white muscle.
A variety of microorganisms are able to produce biogenic amines. The production of cadaverine and putrescine by microorganisms is not surprising since the covalent linking of cadaverine and putrescine to the peptidoglycan is necessary for normal microbial growth (Suzuki and others 1988). Several inoculation studies on both culture media and on fish have demonstrated that Morganella spp., Proteus morganii, Proteus spp., Hafnia alvei, and Klebsiella spp. are able to produce histamines and other biogenic amines. The majority of the studies also concurred that the potential of these microorganisms to produce toxic levels of biogenic amines is enhanced at abusive temperatures (see section 4.2 of this chapter).
The following tables summarize research on production of biogenic amines by microorganisms. Tables IV-3 and 4 list studies on production of biogenic amines by bacterial isolates inoculated on different culture media and on fish that may be cold-smoked, respectively. In addition, studies where isolates from fish have been incubated in media and histamine production monitored are listed in Table IV-5. It is noteworthy to point out that spoilage and toxin formation occur due to a variety of microorganisms, and therefore identical storage times for similar fish species may produce varying levels of scombrotoxin.
Okuzumi and others (1990) investigated the relationship between microflora on horse mackerel (Trachurus japonicus) and dominant spoilage bacteria. The results of their study showed that Pseudomonas I/II, Pseudomonas III/IV-NH, Vibrio, and Photobacterium were dominant when high levels of putrescine, cadaverine, and histamine were detected.
|Histamine producers||Histamine concentration||Temperature and time|
|Morganella spp||4,000 ppm (max)||76 h||Aiso and others 1958|
|Morganella spp||1000 ppm 1000 ppm 0 ppm|| |
25 °C for 24 h
25 °C for 19 h followed by 5 °C for 100 h
5 °C for 100 h
|Klausen and Huss 1987|
|Proteus spp||Large||Kimata and others 1960|
|Proteus morganii||>200 nM/ml large||15, 30, 37 °C for <24 h||Taylor and others 1978 Behling and Taylor 1982|
|Enterobacter aerogenes||>200 nM/ml||Taylor and others 1978|
|Klebiella pneumoniae||Large||15, 30, 37 °C for <24 h||Behling and Taylor 1982|
|Hafnia alvei||Large||30, 37 °C for >48 h||Behling and Taylor 1982|
|Citrobacter freundii||Large||30, 37 °C for >48 h||Behling and Taylor 1982|
|Escherichia coli||Large||30, 37 °C for >48 h||Behling and Taylor 1982|
|Lactobacillus (3 strains)||2.2 mg/ml||Masson and others 1996|
|Bacteria||Fish||Histamine (ppm)||Other biogenic amines||Temperature|| |
|Proteus morganii||Tuna||>50 ppm <50 ppm||24, 30 °C 15 °C||Eitenmiller and others 1981|
|Acinobacter||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Aeromonas hydrophila||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Clostridium perfringens||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Enterobacter aerogenes Enterobacter spp.||Spanish mackerel Mackerel (Scomber japonicus)||detectable||>1ppm detectable||0 °C||Middlebrooks and others 1988 Wendakoon and Sagakuchi 1993|
|Hafnei alvei||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Morganella morganii||Spanish mackerel||>1ppm||0 °C||Middlebrooks andothers 1988|
|Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Pseudomonas spp.||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Vibrio alginolyticus||Spanish mackerel||>1ppm||0 °C||Middlebrooks and others 1988|
|Microorganism||Fish||Histamine||Temperature and Time||Reference|
|Proteus morganii|| |
Skipjack (Euthynnus pelamis)
Jack mackerel (Trachurus symmetricus)
|Detected Detected >1,000 ppm||35 °C for 24 h||Kimata and others 1960 Kimata and others 1960 Ababouch and others 1991b|
|Hafnia alvei||Skipjack Jack mackerel||Detected Detected||Kimata and others 1960 Kimata and others 1960|
|Proteus spp.||Skipjack Jack mackerel Sardine||Detected Detected >1,000 ppm||35 °C for 24 h||Kimata and others 1960 Kimata and others1960 Ababouch and others 1991b|
|Detected Detected||Kimata and others 1960 Kimata and others 1960|
|Morganella morganii||Tuna (Thunnus thunnus) Skipjack tuna (Katsuwonus pelamis) Albacore tuna||>1,000 ppm >1,000 ppm >1,000 ppm||37 °C for 18 h 7, 19, 30 °C for 24 h 15, 25 °C||Lopez-Sabater and others 1994b Arnold and others 1980 Kim and others 2000|
|Klebsiella spp.||Tuna||>1,000 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Enterobacter aerogenes and E. cloacae||Tuna||500-1,000 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Citrobacter freundii||Tuna||<250 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Proteus mirabilis||Tuna||<250 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Proteus vulgaris||Tuna Sardine||<250 ppm >1,000 ppm 100-2,000 ppm||37 °C for 18 h 7, 19, 30 °C, 24 h 35 °C for 24 h||Lopez-Sabater and others 1994b Arnold and others 1980 Ababouch and others 1991b|
|E. agglomerans||Tuna||<250 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Serratia liquifaciens||Tuna||<250 ppm||37 °C for 18 h||Lopez-Sabater and others 1994b|
|Providencia stuarti||Sardine||150-1,000 ppm||35 °C for 24 h||Ababouch and others 1991b|
|Vibrio spp.||Sardine||100 ppm||35 °C for 24 h||Ababouch and others 1991b|
|Stenotrophonas maltophilia||Albacore tuna (Thunnus alalunga)||25.8 ppm >1,000 of other biogenic amines||4 °C for 6 d 37 °C for 24 h||Ben-Gigirey and others 1999|
The activity of decarboxylase can be an indirect measurement of potential for biogenic amine formation. A study by Middlebrooks and others (1988) showed that 14 bacterial isolates (Acinetobacter lowffi, Aeromonas hydrophila, Clostridium perfringens, Enterobacter aerogenes, Enterobacter spp., H. alvei, Morganella morganii, Proteus mirabilis, Proteus vulgaris, Proteus spp., Pseudomonas fluorescens/putida, Pseudomonas putrefaciens, Pseudomonas spp., and Vibrio alginolyticus) from mackerel tissue were capable of exhibiting decarboxylase activity (production of histamine, cadaverine, and putrescine) when incubated in Spanish mackerel at 0 °C (-32 °F), 15 °C (59 °F), and 30 °C (90 °F). Other bacteria strong histidine decarboxylase activities: Klebsiella pneumonia (Taylor and others 1979), Klebsiella planticola (Taylor and Lieber 1979), Alteromonas putrefaciens (Frank and others 1985), Photobacterium phosphoreum (Morii and others 1986); Staphylococcus xylosus (Rodriguez-Jerez and others 1994), Cedecea lapagei, Cedecea neteri, Plesiomonas shigelloides (Lopez-Sabater and others 1994a), Providencia spp. (Ababouch and others 1991b), Lactobacillus curvatus LTH 975 and Lactobacillus buchneri LTH 1388 (Leuschner and Hammes 1999), Serratia spp. (Lopez-Sabater and others 1996a), and Escherichia spp. (Gale 1946).
Okuzumi and others (1984) studied histamine-forming bacteria in addition to N-group (psychrophilic halophilic, histamine-forming) bacteria in and on fresh fish. The histamine-forming bacteria were N-group bacteria, P. morganii, P. vulgaris, H. alvei, Citrobacter spp., Vibrio spp., and Aeromonas spp. For the summer samples, P. morganii was found most frequently, followed by the N-group bacteria. On the other hand, for the winter samples, only the N-group bacteria were found, and other histamine bacteria were not detected.
Changes in the concentration of tyramine, agmatine, putrescine, cadaverine, spermidine, tryptamine, spermine, histamine, and trimethylamine were studied in parallel with the development of the microbial population and sensory scores during the storage of Mediterranean gilt-head sea bream (Sparus aurata) at three temperatures (0 °C [32 °F)] 8 °C [(46 °F] 15 °C [59 °F]) (Koutsoumanis and others 1999). Pseudomonads and H2S-producing bacteria were dominant microorganisms. Enterobacteriaceae and lactic acid bacteria were also present in the fish microflora. Among the biogenic amines, putrescine and cadaverine were detected when pseudomonads exceeded 106 to 107 cfu / g. Histamine was produced only in samples stored at 15 °C and reached >50 ppm levels at 48 h. Putrescine and cadaverine reached high levels also at 15 °C after 120 h. Tyramine, tryptamine, agmatine, and trimethylamine were absent regardless of the storage temperature. The authors concluded that only putrescine and cadaverine could be used as an index of freshness. The role and significance of putrescine and cadaverine in food safety and biogenic amine poisoning is yet to be established. Furthermore, in prevalence studies, researchers are challenged regularly to select or obtain samples that are representative of the existing total population of fish, muscle, microorganisms, or whatever is being studied.
4. Effect of processing steps
4.1. Gutted versus ungutted fish
Before cold smoking, fish often will be eviscerated. Data on the effect of evisceration on biogenic amine production is inconsistent. The rates of biogenic amine (cadaverine and putrescine) formation in fish can be summarized as follows: whole ungutted fish >fillets from whole ungutted fish; fillets >whole gutted fish (Haaland and others 1990). However, this general scheme could be different if fish were processed under varying sanitary conditions. Research by Fernandez-Salguero and Mackie (1987a) reported that histamine, cadaverine, and putrescine were produced more rapidly in haddock fillets than the whole gutted fish and that ungutted fish spoiled more rapidly than fillets. Dawood and others (1988), however, reported that eviscerated fish contained lower concentrations of amines than whole samples of rainbow trout (Salmo irideus, renamed Oncorhynchus mykiss). When gutted and ungutted mackerel (Scomber scombrus) were subjected to two treatments (iced immediately after catching vs. left on the vessel deck at ambient temperature 6 °C - 12 °C [43 - 53 °F]) (Hardy and Smith 1976), processing did not appear to influence histamine formation and histamine contents were low and increased subsequent to spoilage in both gutted and ungutted fish.
4.2 Effect of post-harvest handling
T he most important factor that contributes to the production of biogenic amines during post-harvest handling is the storage time at specific temperatures. Both the post-mortem formation of amino acids and their rapid decarboxylation are temperature-dependent (Haaland and others 1990). While most amino acids were present at higher levels at 2 °C (35 °F) than at 20 °C (68 °F), however, amine formation was greater at 20 °C than at 2 °C.
The effect of temperature on histamine formation has frequently been studied. Table IV-6 lists selected research studies where fish were kept either in ice, refrigerated, or at abusive temperatures for different storage times. Different studies reported that skipjack tuna that was allowed to spoil under similar conditions had 100-fold variations in histamine concentrations. Although there is great variability in the results within the same study, longer storage times and higher temperatures seem to induce histamine production.
|Fish||Temperature/time||Histamine content (ppm)||Other biogenic amines||Sensory||Reference|
|10 °C for 14 d||Not detected||Spoilage||Crapo and Himelbloom 1999|
Tuna (Thunnus thunnus)
Albacore tuna (whole fish)
iced for 33 d
15 - 23 °C for 24 h
15 - 23 °C for 4 d
25 °C for 7 d
Lopez Sabater and others (1996b)
Price and others (1991)
Ben-Gigirey and others (1998b)
|Rainbow trout (Salmo irideus)||0 °C for 24 d||<1||<1||Dawood and others (1988)|
4 h at ambient T
8 d in ice
|Ababouch and others (1991b)|
|Mahimahi (Coryphaena hippurus)|| |
21 °C for 2 d
32 °C for 12 h
32 °C for 24 h
|Baranowski and others (1990)|
|Sardine, saury pike, mackerel, horse mackerel|| |
5 °C for 6 - 9 d
20 °C for 2 d
35 °C for 2 d
|Yamanaka and others (1984)|
|Sardine (Sardina pilchardus), horse mackerel (Trachurus trachurus), chub mackerel (Scomber japonicus), and mackerel (Scomber scombrus)|| |
iced for 7 d
iced for 7 d
iced for 7 d
Mackerel (Scomber scombrus)
Spanish mackerel (Scomberomorus maculatus
Mackerel (Scomber scombrus)
0 °C for 25 d
2 °C for 12 d
10 °C for 120 h
23 °C for 36 h
6 °C for 150 - 200 h
17 °C for 75 h
23 °C for 46 h
35 °C for 20 h
24 °C for 2 d
0 °C for 10 d
10 °C for 4 d
10 °C for 2d and 8d at 0 °C
500 - 700
Fernandez Salguero and Mackie (1979)
Kimata and Kawai (1953)
Edmunds and Eitenmiller (1975)
Klausen and Huss (1987)
|Kahawai||15 - 23 °C for 2 d||1,500 - 3,500||Ben-Gigirey and others (1998b)|
|Herring, Clupea harengus pallasi||10 °C for 14 d||55||Spoiled by 6 d||Crapo and Himelbloom (1999)|
Post-harvest handling conditions have a significant effect on the presence and concentration of putrescine and cadaverine. Ababouch and others (1991b) reported that bacteria on the skin and gills of freshly harvested sardines (Sardina pilchardus) quickly invaded and grew within the muscle tissue, reaching 5 x 108 cfu / g and 6 x 108 cfu / g respectively after 24 h at ambient temperature and 8 d in ice. Histamine, cadaverine, and putrescine accumulated to levels of 2,350 ppm, 1,050 ppm, and 300 ppm respectively after 8 d of ice storage but only 24 h at ambient temperature.
Dawood and others (1988) showed that initial holding temperatures above 0 °C (32 °F) resulted in increased concentrations of non-volatile amines in freshly caught whole and eviscerated rainbow trout (Salmo irideus). In another study on skipjack tuna (Euthynnus lineatus), Mazorra-Manzano and others (2000) concluded that endogenous and microbial deterioration processes could be controlled at 0 °C, since, even after 24 d, there was <1 ppm of any of the biogenic amines analyzed (histamine, cadaverine, and putrescine) in hook- and line-caught fish that were immediately iced upon landing. Consistent with those results, Atlantic herring (Clupea harhengus) and Atlantic mackerel (Scomber scombrus) contained insignificant amounts (<3 ppm) of cadaverine and putrescine after 7 and 3 d of iced (1 °C, 34 °F) storage (Ritchie and Mackie 1980). These reports are in contrast to an earlier one, where the histamine content of albacore tuna was reported as 7.5 mg/100 g (75 ppm) of fresh fish during unloading from a fishing vessel (Leitao and others 1983) and 82.5 mg/100 g (825 ppm) after 33 d of ice storage (Price and others 1991). (These high values may be indicative of mishandling on the fishing vessel and the resulting fish decomposition). Also, Shewan and Liston (1955) reported that histidine was easily decarboxylated at 0 °C (32 °F). The variability of these findings reflects the challenges of representative sampling, species differences, quality of initial raw material, and other experimental conditions. Nevertheless, control of biogenic amine production by low temperatures (for example, 0 °C, 32 °F) is a constant observation.
Klausen and Huss (1987) found no histamine formation in mackerel stored in ice, whereas a rapid increase was noted at 10 °C (50 °F). Interestingly, storage at 10 °C for 2 d with no detectable histamine formation and subsequent storage at 0 °C (32 °F) led to formation of 200 ppm histamine after 8 d. These studies indicate that although the histamine-forming bacteria do not grow at 0 °C, decarboxylase formed during growth at 10 °C may be active at 0 °C.
Temperature-abuse potentiates histamine formation in fresh mahimahi (Coryphaena hippurus) at 32 °C (86 °F) increasing from 1.6 ppm to 2,920 ppm in 24 h (see Table IV-11) (Baranowski and others 1990). In a second study, Baranowski and others (1990) showed that heat penetration was much more rapid during incubation in seawater than in air, affecting the histamine content and quality score of the fish (Table IV-7).
|Storage Condition*||Histamine (ppm)||Quality Score**|
*Four (4) fish per treatment
**Decreasing 10-point scale where 10 - 9 = fresh, acceptable; 8 - 6 = slight decomposition; 5 - 3 = definite decomposition; and 2 - 1 = advanced decomposition
The histamine formation of big eye tuna (Thunnus obesus) and skipjack (Katsuwonus pelamis) tuna during storage at 4 °C (39 °F), 10 °C (50 °F), and 22 °C (72 °F) occurred very quickly at 22 °C, exceeding 50 mg / 100 g (500 ppm) in 1 d for skipjack and 2 d for big eye tuna (Silva and others 1998). The rise in histamine content was delayed at refrigerated temperatures (10 °C and 4 °C), but notable amounts were detected after 3 d at 10 °C and 6 d at 4 °C (Table IV-8).
|Histamine in Skipjack||Histamine in Big Eye Tuna|
|Days||4 °C||10 °C||22 °C||4 °C||10 °C||22 °C|
The changes in histamine content during storage at 5 °C (44 °F), 20 °C (68 °F), and 35 °C (95 °F) were examined in the ordinary and dark meats of sardine, saury pike, mackerel, yellowtail, skipjack, big eye tuna, and horse mackerel (Yamanaka and others 1984). During storage at 20 °C and 35 °C, histamine was produced and accumulated >500 ppm levels at 2 - 6 d of storage, depending on the species. During 5 °C storage, however, the amounts of histamine gradually increased up to those levels in 9 d in sardine, saury pike, mackerel, and horse mackerel. Histamine formation in dark meat was less than that in white meat at the same temperature.
Recently, changes in histamine, cadaverine, putrescine, and agmantine contents were examined in sardine (Sardina pilchardus), Atlantic horse mackerel (Trachurus trachurus), chub mackerel (Scomber japonicus), and Atlantic mackerel (Scomber scombrus) during ice storage (2 - 3 °C, 35 - 37 °F) and storage at room temperature (20 - 23 °C, 68 - 73 °F) (Mendes 1999). At day 0, the initially high aerobic colony counts were 105 - 106 cfu / g. They reached a maximum within 48 - 55 h in fish stored at 22 - 23 °C, but only after prolonged times (10 - 16 d) in fish at 2 - 3 °C. Histamine formation, as well as other amines, varied greatly with species of fish and storage conditions. The levels of histamine, cadaverine, and putrescine increased gradually in all species as decomposition progressed, regardless of storage temperatures, and reached maximum limits for human consumption after 24 h of storage at room temperature. In contrast, amine production in iced fish was considerably reduced and histamine concentration increased slowly until day 7, after which a significant rise was detected, but generally was below 100 mg / Kg. No correlation was observed for histamine or other amine levels and the degree of fish decomposition. Consequently, the belief that decomposition protects consumers from hazardous biogenic amines seems disputable. Again in contrast, a recent report (Kaneko 2000) described the development of a Hazard Analysis Critical Control Point (HACCP) approach using Vessel Standard Operating Procedures for control of histamine on Hawaiian fishing vessels. They concluded that odors of decomposition were reliable indicators of histamine risk and that sensory evaluation is an effective HACCP control measure in the Hawaiian fishery. In this study, 583 mixed pelagic fish (fresh bigeye, yellowfin, albacore tuna, striped marlin, blue marlin, and mahimahi stored in ice) were sampled at the time of delivery from commercial fishing vessels. Fish were graded for quality, by using sensory indicators of decomposition, and analyzed for histamine concentration. A total of 119 fish were rejected because of decomposition. Only 14 fish exceeded 5mg / 100 mg (50 ppm) histamine defect action limit. All 14 fish were first rejected from the market because of odors of decomposition. None of the fish that passed the sensory evaluation exceeded the defect action limit. These conflicting results pose a challenge if biogenic amines are to be used as legal safety indices. Another challenge is to develop an acceptable definition for an odor of decomposition.
It is imperative to recognize that the fish species affect the production of biogenic amines and that many species are rarely, if ever, currently utilized in cold-smoked fish products. Variable and differing data are frequently reported. For instance, 34 albacore tuna (Thunnus alalunga) samples left on the deck (deck temperature 15.5 - 23.5 °C, 59 - 73 °F) for <12 h contained negligible histamine (<0.40 mg/100 g muscle [4 ppm]). Four samples left on the deck for up to 24 h did not contain any significant amounts of histamine (<0.18 mg / 100 g [1.8 ppm]). Among 9 fish left at up to 4 d, only 2 exhibited histamine levels higher than 5.0 mg / 100 g (50 ppm), that is, 9.31 and 6.19 mg/100 g (93.1 and 61.9 ppm) (Ben-Gigiery
Fresh pink salmon (Oncorhynchus gorbuscha) fillets and whole Pacific herring (Clupea harengus pallasi) were stored for 2 wk at 10 °C (50 °F) to determine if significant amounts of histamine were produced prior to spoilage (Crapo and Himelbloom 1999). Spoilage odors in salmon were moderate by day 4 and intense by day 7, while herring had detectable spoilage by day 4 and became potent by day 6. Aerobic colony counts increased from 102 -103cfu / g initially to 107 - 108 cfu / g by day 14. Histamine was not detected in salmon, while concentrations reached 55 ppm in herring at day 14. If spoilage were to be used as protection from histamine poisoning, according to this study, 10 °C would be an appropriate temperature to store salmon and herring, since toxic levels were not reached before spoilage occurred. Again caution must be taken because variability among many of the findings on decomposition-histamine relationships reflect the challenges of representative sampling, species differences, and other experimental conditions.
The effect of temperature has also been investigated through inoculation studies with histamine-producing bacteria. Biogenic amine concentrations and sensory changes in fresh and Morganella morganii inoculated blue fish (Pomatomum saltatrix) stored at 5, 10, and 15 °C (41, 50, and 59 °F) were reported by Gingerich and others (1999). Histamine content in fresh fish ranged from <1 to 99 ppm, with an average of 39 ppm. Putrescine and cadaverine were not present. Within 5 d of storage, high concentrations of histamine occurred while the fish were judged acceptable for consumption by the sensory panel. Kim and others (2000) isolated histamine-producing bacteria from albacore tuna stored at 0, 25, 30, and 37 °C (32, 77, 90, 98 °F). The optimum temperature for growth of histamine-producing bacteria was 25 °C. The bacterium producing the highest level of histamine isolated from fish abused at 25 °C was identified as M. morganii. The M. morganii isolate was inoculated into tuna fish infusion broth medium, and the effect of temperature was determined for microbial growth and formation of histamine and other biogenic amines. The isolate produced the highest level of histamine, 5,253 ppm, at 25 °C in the stationary phase. At 15 °C, histamine production was reduced to 2,769 ppm. Neither microbial growth nor histamine formation was detected at 4 °C. Cadaverine, putrescine, and phenylethylamine were also detected. The optimum temperature for histamine, cadaverine, putrescine, and phenylethylamine formation was 25 °C.
Histamine production by P. morganii, P. vulgaris, and H. alvei cultures isolated from skipjack tuna (Katsuwonus pelamis) was measured at storage temperatures of 1, 7, 19, and 30 °C (4, 44, 66, 90 °F) in skipjack infusion broth (Arnold and others 1980). The highest histamine concentrations were observed at 19 and 30 °C depending on the bacterial species (Table IV-9). No histamine was formed at 1 °C, indicating that rapid cooling of tuna flesh may adequately suppress histamine formation. At 19 °C and 30 °C, the Proteus organisms at first formed high levels of histamine, much of which was subsequently destroyed. It appears the histamine concentration may eventually depend on an equilibrium between histamine production and destruction. The authors noted that their conclusion was similar to that of other investigators who reported that tuna flesh homogenate incubated at 25 °C was able to produce approximately 600 mg / 100 g (6,000 ppm) histamine on day 1 but only 350 mg / 100 g (3,500 ppm) remained on day 3. However, this study was performed in an infusion broth and not in fish muscle, which may have changed the results.
|30 °C||19 °C||7 °C|
Post-harvest antimicrobial treatments did not show much promise in inhibiting histamine formation. Fish were incubated in seawater (off the coast of Hawaii) and in seawater containing 100 ppm of sodium hypochlorite or chlorine dioxide; however, neither histamine formation nor quality loss was inhibited (Table IV-10) (Baranowski and others 1990).
|Incubation medium*||Histamine (ppm)||Quality Score**|
|SW + sodium hypochlorite||2,340||3.0|
|SW + chlorine dioxide||2,360||2.5|
*Four (4) fish per treatment.
**Decreasing 10-point scale where 10 - 9 = fresh, acceptable; 8 - 6 = slight decomposition; 5 - 3 = definite decomposition; and 2 - 1 = advanced decomposition
Albacore tuna (Thunnus alalunga) specimens of high quality were analyzed for their biogenic amine contents after 1, 3, 6, and 9 mo of frozen storage at -18 °C (-0.4 °F) or -25 °C (-13 °F) by Ben-Gigirey and others (1998a). Putrescine showed the greatest increase, reaching concentrations of 59 ppm (815% of the initial level) and 68 ppm (942% of the initial level) in the white muscle after 9 mo of storage at -18 °C and -25 °C, respectively. Cadaverine, histamine, and spermidine concentrations were below 3, 5, and 11 ppm respectively after 9 mo of frozen storage.
Fresh mackerel (Scomber scombrus) with no detectable histamine contained 3, 51, and 53 mg / kg (3, 51, and 53 ppm) when stored at -20 °C (-4 °F) for 11, 22, and 33 wk, respectively (Zotos and others 1995). This is in contrast to a report by Hardy and Smith (1976) who stored high quality mackerel (Scomber scombrus) at -14, -21, and -29 °C (7, 6, -20 °F) for 72 wk (1.5 years) and reported no measurable histamine formation.
Studies on the effect of incubation at 32 °C (86 °F) after frozen storage for 24 wk showed that histamine levels were greatly reduced (Table IV-11). Furthermore, fish frozen for 40 wk had almost no histamine formation during incubation suggesting that its microflora had undergone a greater reduction that occurred during the 24-wk storage period (Baranowski and others 1990).
|H at 32 °C|
|Frozen storage* (wk)||Histamine (ppm)|
*Four (4) fish per treatment.
**Decreasing 10-point scale where 10 - 9 = fresh, acceptable; 8 - 6 = slight decomposition; 5 - 3 = definite decomposition; and 2 - 1 = advanced decomposition
The findings of Baranowski and others (1990) may be explained by the data of Fujii and others (1994) and Mendes and others (1999). The specific activity of histidine-decarboxylase of halophilic histamine-forming bacteria, Photobacterium phosphoreum and Photobacterium histaminum, remained at 27 - 53% of the initial value after 7 d of storage at -20 °C (-4 °F) (Fujii and others 1994). During this time the viable cells decreased by more than 6 log cycles of the initial counts. Similarly, Mendes and others (1999) reported that freezing sardines (Sardina pilchardus) reduced the numbers of bacteria capable of forming biogenic amines; however, even when the post-freezing viable count of histamine-forming bacteria is low, earlier reports (Yamanaka and others 1982; Karolus and others 1985; Yamanaka and others 1987b) suggested the possibility that if the fish had been temperature-abused before freezing, histamines may still be present in toxic amounts. Therefore, it is extremely important to know the temperature history of the frozen fish, since outbreaks of scombroid fish poisoning can be caused by the ingestion of frozen-thawed fish containing degradation products if the fish were previously temperature-abused.
Taylor and Speckhard (1984) reported that NaCl at levels up to 2% were ineffective in preventing M. morganii and Klebsiella pneumonia growth and histamine production in TSBH medium. Henry Chin and Kohler (1986) indicated that high levels of salt concentration (3.5% - 5.5% NaCl) could inhibit the histamine production by histamine-forming bacteria. Ababouch and others (1991a), however, reported that sprinkling salt on sardines at a level of 8% (w/w) increased lag phase for total bacteria at room temperature but not in ice. Generation time of histamine producers and lag phase increased at room temperature and ice storage, respectively (Table IV-12). Salt seems to have an inhibiting effect on histamine producers at either temperature.
|Storage at ambient temperature 24 - 28 °C||Storage in ice|
|0% NaCl||8% NaCl||0% NaCl||8% NaCl|
|Lag phase (h)||Generation time (b)||Lag phase (h)|| |
|Lag phase (h)||Generation time (h)||Lag phase (h)||Generation time (h)|
|Hist Prod Bac||0||1.9||0||7.0||24||13.6||77||13.2|
A subsequent study by Leroi and others (2000) showed that the inhibition of bacteria in cold-smoked salmon stored for 5 wk at 5 °C (41 °F) and salt (5% wt/wt) and smoke was linearly proportional to the salt and smoke content (the higher the concentration, the greater the inhibition). No synergistic inhibition effect was observed between the two factors.
4.5 Smoked product
Gessner and others (1996) reported a scombrotoxicosis-like illness occurring in an individual within 10 min after eating a 25 g strip of home-smoked sockeye salmon. The meat came from 1 of 8 salmon caught and stored in a cooler for up to 12 h. Strips cut from the fish bellies had been placed in saltwater brine for 7 min, cooled with a fan for 6 h, and smoked for 2 d at a maximum temperature of 38 - 44 °C (100 - 111 °F) using untreated alder chips. A random sample of 6 strips was tested by the FDA and showed a mean histamine level of 0.19 mg / 100 g; a mean putrescine level of 0.67 mg / 100 g; and a mean cadaverine level of 0.19 mg / 100 g. Two fish strips had water phase salt concentrations of 2.7% and 2.1%. The patient ate an estimated 0.0006 mg of histamine/kg of body weight, well below the estimated 1 mg of histamine/kg of body weight reported to cause illness. The authors did not give a reason for this apparent high sensitivity to such a low concentration of histamine. This reported illness of a single individual is contrary to other published information on histamine toxicity. Also, the samples tested may not have represented the product consumed by the subject of the illness.
The production of biogenic amines during chill storage (5 °C, 41°F)) of cold-smoked salmon (Salmo salar) from 3 smoke houses over a 2-year period (1997 and 1998) was studied by Jorgensen and others (2000). Results of the study showed the production of biogenic amines is unlikely to result in histamine poisoning in humans as indicated by epidemiological data (Table IV-13). Some samples exceeded the defect action level of 50 ppm established by the FDA for Scombridae and 100 - 200 ppm by E.U. regulations for Scombridae and Clupeidae, but no samples reached toxic levels of 500 ppm, a value at which one would expect illness and that the FDA would use in legal proceedings (EEC 1991; FDA 1998).
|Salting||Brine injection||brine injection||dry salting|
|Ingredients||NaCl||NaCl, sucrose||NaCl, nitrite, sucrose|
|Drying||3 - 4 h, |
no humidity control
|no separate drying process||6 - 12 h, 27 °C, 50% relative humidity|
|Smoking||4 h, |
no humidity control
|4 - 7 h, 21-22 °C, no humidity control||6 - 12 h, 27 °C, 65% relative humidity|
|initial pH||6.09 ± 0.02a||6.09 ± 0.01||6.14 ± 0.04||6.01 ± 0.02||6.11 ± 0.01||6.07 ± 0.04||6.13 ± 0.07||6.00 ± 0.04||6.08 ± 0.02||6.11 ± 0.05||6.16 ± 0.03||6.11 ± 0.03|
|NaCl (% WPS)||5.4 ± 0.4||5.0 ± 0.5||4.9 ± 0.2||4.1 ± 0.5||7.5 ± 0.6||5.9 ± 0.4||4.2 ± 0.3||4.2 ± 0.6||7.9 ± 1.3||5.6 ± 0.5||3.9 ± 0.5||4.9 ± 0.7|
|NaNO2 (ppm)||<0.6||<0.6||<0.6||<0.6||<0.6||<0.6||<0.6||<0.6||16 ± 7||22 ± 10||8 ± 5||12 ± 8|
|shelf life (ws)||4 - 5||4.5 - 5||4 - 5||4.5 - 5.5||8.5 - 9||7 - 8||3 - 4||5.5 - 6.5||5 - 6||4.5 - 5||4 - 4.5||5.5 - 6.5|
|characteristics at time of spoilage|
|Ph||6.10 ± 0.01||6.23 ± 0.05||6.06 ± 0.04||5.98 ± 0.03||5.95 ± 0.08||5.64 ± 0.2||5.70 ± 0.18||5.63 ± 0.03||6.06 ± 0.08||6.18 ± 0.02||5.90 ± 0.06||5.99 ± 0.19|
|biogenic amines (ppm)|
|Agmatine||234 ± 107||220 ± 118||29 ± 26||121 ± 25||18 ± 7||2 ± 1||88 ± 24||32 ± 30||142 ± 179||270 ± 90||25 ± 13||2 ± 1|
|Cadaverine||265 ± 72||251 ± 63||135 ± 69||345 ± 95||36 ± 11||101 ± 27||152 ± 70||131 ± 135||168 ± 170||277 ± 33||178 ± 66||303 ± 140|
|Histamine||135 ± 73||190 ± 130||3 ± 3||96 ± 20||19 ± 27||4 ± 2||102 ± 15||50 ± 41||108 ± 118||240 ± 64||10 ± 6||16 ± 10|
|Putrescine||11 ± 4||3 ± 1||11 ± 9||28 ± 16||31 ± 16||8 ± 6||7 ± 3||40 ± 34||33 ± 32||32 ± 18||190 ± 64||383 ± 32|
|Tyramine||137 ± 63||228 ± 23||180 ± 10||235 ± 15||202 ± 21||128 ± 42||82 ± 29||158 ± 74||108 ± 102||235 ± 40||223 ± 33||335 ± 31|
|off-flavors||Sour,c bitter, fishy, rancid||sour, faecal, rancid||sour, faecal||sour, faecal||rancid, sour||sour, chemical||sour||sour, faecal||sour, faecal||sour, faecal||sour, faecal|
|Texture||pasty, sticky||soft, sticky||soft, sticky||soft, sticky||soft||soft||soft||soft||soft||soft||soft||soft|
|microflora, log10 (CFU/g)|
|TPC||6.9 ± 0.1||7.6 ± 0.2||7.3 ± 0.3||7.6 ± 0.2||8.2 ± 0.4||8.7 ± 0.3||7.8 ± 0.4||8.5 ± 0.1||6.9 ± 0.3||7.2 ± 0.2||8.3 ± 01||8.5 ± 0.2|
|LAB||6.8 ± 0.2||7.5 ± 0.1||7.6 ± 0.1||7.8 ± 0.2||8.1 ± 0.4||8.5 ± 0.3||8.6 ± 0.1||8.7 ± 0.2||6.8 ± 0.3||7.1 ± 0.2||8.4 ± 0.1||8.4 ± 0.3|
|Enterobacteriaceae||4.1 ± 1.0||6.7 ± 0.6||6.1 ± 0.2||6.1 ± 0.8||<3.0||6.5 ± 0.5||3.4 ± 1.0||6.1 ± 1.5||<3.0||4.2 ± 1.6||5.9 ± 1.4||6.5 ± 0.8|
|a Average ± standard deviation of 3 or 4 individual packs, lots 97-1 to 97-6 and 98-1 to 98-6, respectively|
b Profile of biogenic amines (PBA).
c Attributes responsible for spoilage are indicated in italics.
Although the temperatures used for a hot-smoking process may inhibit histamine producers, cold-smoking does not expose the fish to temperatures high enough to inhibit the latter bacteria. The effect of hot-smoking previously frozen mackerel (Scomber scombrus) on histamine formation was reported by Zotos and others (1995) (Table IV-14). Smoking was done for a total of 7 h, at sequential temperatures of 30, 40 and 70 °C. From Table IV-14 it can be observed that a significant (p >0.05) increase in histamine formation in fresh, frozen (11 or 33 wk) mackerel was solely due to the smoking process. The histamine increase appeared to be independent of frozen storage time prior to smoking. Although this is a hot smoking process example, it demonstrates the importance of controlling the temperature and time of the smoking process.
|Sample||Thaweda (mg histamine kg-1)||Smokeda (mg histamine kg-1)|
|Fresh||0.0||42.0 ± 0.45|
|Frozen 11 wk||3.0 ± 0.05a||44.0 ± 0.16|
|Frozen 22 wk||51.0 ± 0.56||63.0 ± 0.67|
|Frozen 33 wk||53.0 ± 0.34||94.0 ± 0|
|a Dry, salt-free sample (sic)|
In many situations the production of biogenic amines is highly variable and difficult to predict. For example, cold-smoked, fermented rainbow trout (Oncorhynchus mykiss) were prepared with 3 different lactic acid bacteria (LAB) inocula plus staphylococci, with the control group being prepared without inoculum (Petaja and others 2000). The fish were cured by injecting brine (20% NaCl, 18% glucose, 0.5% ascorbic acid, and 0.625% KNO3) at amounts corresponding to 5% of the weight of the fish fillet. The lactic acid bacteria inoculum was at 107 cfu / g and staphylococci at 5 x 106 cfu / g. The products were acceptable by sensory analysis, the LAB inoculum grew to >108 cfu / g, the pH reduced to 5.0 - 5.3, and aw to 0.927 and the pseudomonads, the predominate flora, disappeared. The fish raw material and products contained low amounts of biogenic amines with one exception: cadaverine, histamine, and tyramine increased in all product groups except in one experimental series (II) out of three (Table IV-15). This broad variability was again evident in this report.
Microbiological, chemical, and sensory changes in cold-smoked salmon were studied during 5 wk of vacuum storage at 5 °C (41 °F) (Leroi and others 1998). Total aerobic colony counts reached 3 x 106 after 6 d; however, the shelf life was judged by a sensory panel to be acceptable for 2-3 wk. During the first 2 wk, gram-negative bacteria were dominant, mainly represented by Swanella putrefaciens immediately after the smoking process and then Photobacterium phosphoreum. Aeromonas spp. were present throughout the storage but in smaller amounts. Gram-negative bacteria then progressively decreased while gram-positive bacteria increased, dominated by LAB. A diversification was observed at the end of storage, with the appearance of Lactobacillus farciminis, Lactobacillus sake, and Lactobacillus alimentarius.
|Amine||Fish fillet group||0 day||3 days||35 days|
|3 MLHK|| |
|POHK pediococcus strain POHK and Pökelferment 77 starter; MLHK pediococcus strain MLHK and Pökelferment 77 starter; CC-430 starter.|
Three bacterial suspensions (final concentrations for Klebsiella oxytoca T2, 5.6 x 106/ml; M. morganii JM, 1.3 x 106 / ml; H. alvei T8, 1.2 x 106 / ml) were used by Wei and others (1990) to inoculate yellowfin tuna (Thunnus albacares). Vacuum- and nonvacuum-packaged samples were stored at 2 and 10 °C (50 °F) and examined for growth and histamine formation on days 3, 6, 10, and 15. The bacteria were also placed in culture and incubated at 3, 5, 7, 120, 15, or 25 °C (37, 41, 44, 248, 59, 77 °F) for a maximum of 10 d. Spiked tuna stored at 2 °C contained <12 mg / 100 g (120 ppm) histamine while samples stored at 10 °C had high levels, >200 mg / 100 g (2,000 ppm). The lowest temperature at which K. oxytoca T2, K. morganii JM and H. alvei T8 produced histamine was 7, 7, and 20 °C, respectively, and for growth was 5, 7, and 3 °C, respectively. Vacuum packaging did not show any beneficial effect in controlling histamine production and bacterial growth. Low temperature storage was more effective than vacuum packaging.
Reddy and others (1992) reported that the growth of common aerobic spoilage bacteria from genera such as Pseudomonas, Flavobacterium, Micrococcus, and Moraxella are inhibited by CO2 in MA-packaged fish during refrigerated storage. Inhibition of these common spoilage psychrotrophic bacteria increases the shelf life, permitting a different type of spoilage flora (that is, the slower-growing gram-positive bacteria, including Lactobacillus spp). The inhibition of the gram-negative bacteria by modified atmosphere packaging may result in an initial reduction rate of histamine formation, thereby providing some increased control on raw material for cold-smoked fish product.
4.7 Other miscellaneous considerations
Taylor and Speckhard (1984) observed that potassium sorbate at a concentration of 0.5% inhibited growth and histamine production of the bacteria in the same medium at both 10 °C (50 °F) for up to 216 h and 32 °C (86 °F) for up to 120 h.
The histamine content of mackerel fillets inoculated by dipping for 30 s in a 7.5 x 103 cfu/ml suspension of M. morganii and stored for 8 d at 4 °C (39 °F) with combinations of NaCl, potassium sorbate and modified atmospheric packaging (MAP) were measured (Aytac and others 2000). Samples treated with 1% potassium sorbate solution contained histamine content lower than a control during 2 d of storage. MAP combined with 1% potassium sorbate also retarded the growth of M. morganii during 3 d, when compared to the control. After 3 d, M. morganii counts were 1.2 x 105 / g, 5 x 105 / g, and 8 x 105 / g for 100% CO2, 100% CO2 combined with 1% potassium sorbate, and control, respectively. Although when CO2 was used alone, histamine production was slower than in the control, it reached higher levels than the control after 8 d (198 mg / 100 g [1,980 ppm] in the CO2 stored group versus 75.2 mg / 100 g [752 ppm] in the control). It appears that after longer times of storage, none of the treatments was effective in controlling the formation of biogenic amines. It is apparent that the shelf-life extension of MAP fish can be extended only if sanitary conditions combined with proper temperature are maintained from harvest.
The histamine content of irradiated samples increased gradually during storage at 4 °C (39 °F) of mackerel samples inoculated for 30 s in a 7.5 x 103 cfu/ml suspension of M. morganii (Aytac and others 2000). Maximum histamine levels after 8 d were 202 mg / 100 g (202 ppm) and 206 mg / 100 g (2,06 ppm) for the samples irradiated with the doses of 0.5 and 2.0 kGy respectively, compared to an initial concentration of 41.2 mg / 100 g (412 ppm). M. morganella grew approximately 2.0 and 0.7 logs in samples irradiated with 0.5 kGy and 2.0 kGy during 8 d. This is in contrast to Mutluer and others (1989), who concluded that irradiation using 1.0 and 2.0 kGy, in conjunction with refrigeration at 5 °C (41 °F), effectively retarded production of histamine for a 10-day period in mackerel fillets inoculated with M. morganii. Again, the variability of these findings reflects the challenges of representative sampling, species differences, quality of initial raw material, and other experimental conditions.
The following are conclusions about the potential for cold-smoked fish consumption to result in scombrotoxin foodborne illness:
- The majority of species that are cold-smoked have not been identified by the scientific community as causing scombrotoxin illness. Therefore, the risk of food-borne illness is limited in the majority of cold-smoked products available in the marketplace.
- Only relatively high and sometimes controversial concentrations of histamine have usually resulted in illness. The contribution of other biogenic amines to the onset of symptoms is not well understood.
- Most scombrotoxin results from extrinsic, rather than intrinsic, spoilage through the growth of certain bacteria, generally members of the family Enterobactericae. Some bacteria are capable of producing greater quantities of decarboxylase enzymes than others.
- Certain processing operations, such as freezing, salting or smoking may be capable of inhibiting or inactivating biogenic amine-producing microorganisms. However, microorganism growth and potential toxun formation may occur after thawing and post processing.
- Under certain conditions addition of lactic acid-producing microorganisms suppresses the growth of biogenic amine-forming microorganisms.
- Vacuum packaging does not prevent growth of biogenic amine-forming microorganisms.
- While biogenic amine-forming microorganisms may grow at refrigeration temperatures, generally the minimal temperature for growth is lower than the minimal temperature for toxin production.
- The most effective methods of preventing biogenic amine formation are handling and processing under sanitary conditions, rapid cooling of the fish, and continued refrigeration from harvest through consumption.
- Limited research has shown that histamine production is greater in light (white) meat rather than dark (red) meat, but the histidine concentration is greater in the dark meat species of fish.
- Much of the research reported in the scientific literature on scombrotoxin utilized fish samples obtained from processing facilities and retail food stores. Only a limited number of studies followed samples from harvest through analysis. Also, sensory analyses were not always incorporated into microbiological and analytical chemical studies. There is a lack of reports describing comprehensive and integrated projects.
6. Research Needs
The following is a list of research areas that the panel suggests need further attention:
- Determine the influence of modified atmosphere packaging on the inhibition of biogenic amine production by gram-negative bacteria.
- Define the minimum temperatures for growth and biogenic amine production of biogenic amine-forming microorganisms.
- Identify practical temperatures that would minimize the levels of biogenic amines in all steps of the chain production and processing and in the final product.
- Determine the effect of salt and redox potential on the formation of biogenic amines in the final product.
- Determine the impact of inter-relationship(s) among histamine, putrescine, and cadaverine, and perhaps other biogenic amine concentrations in scombrotoxin and their effects on subsequent host responses.
- Investigate the effects of various cold-smoked fish processes (water phase salt concentrations, process times and temperatures) on biogenic amine formation.
- Apply new processes, such as irradiation, modified atmospheres, or high pressure, to reduce specific groups of microorganisms to determine if control of those responsible for biogenic amine formation reduces the hazard.
- Evaluate the effects of harvesting methods and post-harvest handling practices on biogenic amine formation under varying environmental conditions.
- Investigate practical methods for cold-smoked fish processors to determine the histamine/scombrotoxin risk in the raw material used for smoking.
- Identify specific methods for representative and effective sampling and for accurate and precise analysis of biogenic amines.
Ababouch L, Afilal ME, Benabdeljelil H, Busta FF. 1991a. Quantitative changes in bacteria, amino acids and biogenic amines in sardine (Sardina pilchardus) stored at ambient temperature (25-28° C) and in ice. Int J Food Sci Tech 26:297-306.
Ababouch L, Afilal ME, Rhafiri S, Busta FF. 1991b. Identification of histamine-producing bacteria isolated from sardine (Sardina pilchardus) stored in ice and at ambient temperature (25° C). Food Microbiol 8:127-36.
Aiiso K, Toyoura H, Iida H. 1958. Distribution and activity of histidine decarboxylase in Morganella. Jap J Microbiol 2(2):143-7.
Aksnes A. 1988. Location of enzymes responsible for autolysis in bulk-stored capelin (Mallotus villosus). J Sci Food Agric 44:263-71.
Aksnes A, Brekken B. 1988. Tissue degradation, amino acid liberation and bacterial decomposition of bulk stored capelin. J Sci Food Agric 45:53-60.
Arnold SH, Brown WD. 1978. Histamine (?) toxicity from fish products. Adv Food Res 24:113-54.
Arnold SH, Price RJ, Brown WD. 1980. Histamine formation by bacteria isolated from skipjack tuna, Katsuwonus pelamis. Bull Jap Soc Sci Fish 46(8):991-5.
Aytac SA, Ozbas ZY, Vural H. 2000. Effects of irradiation, antimicrobial agents and modified-atmosphere packaging on histamine production by Morganella morganii in mackerel fillets. Archiv Fur Lebensmittelhygiene 51:28-30.
Baranowski JD, Frank HA, Brust PA, Chongsiriwatana M, Premaratne RJ. 1990. Decomposition and histamine content in mahimahi (Coryphaena hippurus). J Food Prot 53(3):217-22.
Behling AR, Taylor SL. 1982. Bacterial histamine production as a function of temperature and time of incubation. J Food Sci 47:1311-4, 1317.
Ben-Gigirey B, Craven C, An H. 1998b. Histamine formation in albacore muscle analyzed by AOAC and enzymatic methods. J Food Sci 63(2):210-4.
Ben-Gigirey B, Vieites Baptista de Sousa JM, Villa TG, Barros-Velazquez J. 1998a. Changes in biogenic amines and microbiological analysis in albacore ( Thunnus alalunga ) muscle during frozen storage. J Food Prot 61(5):608-15.
Ben-Gigirey B, Vietites Baptista de Sousa JM, Villa TG, Barros-Velazquez J. 1999. Histamine and cadaverine production by bacteria isolated from fresh and frozen albacore ( Thunnus alalunga ). J Food Prot 62(8):933-9.
Bjeldanes LF, Schutz DE, Mooris MM. 1978. On the aetiology of scombroid poisoning: cadaverine potentiation of histamine toxicity in the guinea-pig. Food Cosmet Toxicol 16(2):157-9.
Chu C-H, Bjeldanes LF. 1981. Effect of diamines, polyamines and tuna fish extracts on the binding of histamine to mucin in vitro. J Food Sci 47:79-?
Clifford MN, Walker R, Ijomah P, Wright J, Murray CK, Hardy R. 1991. Is there a role for amines other than histamines in the aetiology of scombrotoxicosis. Food Addit Contam 8(5):641-52.
Clifford MN, Walker R, Wright J, Hardy R, Murray CK. 1989. Studies with volunteers on the role of histamine in suspected scombrotoxicosis. J Sci Food Agric 47:365-75.
Crapo C, Himelbloom B. 1999. Spoilage and histamine in whole Pacific herring (Clupea harengus pallasi) and pink salmon (Oncorhynchus gorbuscha) fillets. J Food Safety 19:45-55.
Dawood AA, Karkalas J, Roy RN, Williams CS. 1988. The occurrence of non-volatile amines in chilled-stored rainbow trout ( Salmo irideus ). Food Chem 27:33-45.
Douglas WW. 1970. Histamine and antihistamines; 5-Hydroxytryptamine and antagonists. In: Goodman LS, Gilman A, editors. The pharmacological basis of therapeutics. 5th ed. New York: Macmillan. p 621-62.
Edmunds WJ, Eitenmiller RR. 1975. Effect of storage time and temperature on histamine content and histidine decarboxylase activity of aquatic species. J Food Sci 40:516-9.
EEC. 1991. Council directive 91/493/EEC of 22nd July 1991 laying down the health conditions for the production and the placing on the market of fishery products. Off J Eur Comm(No. L268):15-32.
Eitenmiller RR, Wallis JW, Orr JH, Phillips RD. 1981. Production of histidine decarboxylase and histamine by Proteus morganii. J Food Prot 44(11):815-20.
[FDA] Food and Drug Administration. 1996. Fish & fisheries products hazards & controls guide: first edition. Washington D.C.: FDA, Center for Food Safety and Applied Nutrition, Office of Seafood.
[FDA] Food and Drug Administration. 1998. Fish & Fisheries Products Hazards & Controls Guide. 2nd ed. Washington, D.C.: FDA, Office of Seafood. 276 p.
Fernandez-Salguero J, Mackie IM. 1979. Histidine metabolism in mackerel (Scomber scombrus). Studies on histidine decarboxylase activity and histamine formation during storage of flesh and liver under sterile and non-sterile conditions. J Food Technol 14:131-9.
Fernandez-Salguero J, Mackie IM. 1987a. Comparative rates of spoilage of fillets and whole fish during storage of haddock (Melanogrammus aeglefinus) and herring (Clupea harengus) as determined by the formation of non-volatile and volatile amines. Int J Food Sci Tech 22:385-90.
Fernandez-Salguero J, Mackie IM. 1987b. Technical note: Preliminary survey of the content of histamine and other higher amines in some samples of Spanish canned fish. Int J Food Sci Tech 22:409-12.
Fletcher GC, Summers G, Winchester RV, Wong RJ. 1995. Histamine and histidine in New Zealand marine fish and shellfish species, particularly Kahawai (Arripis trutta). J Aquat Food Prod Technol 4(2):53-74.
Frank HA, Baranowski JD, Chongsiriwatana M, Brust PA, Premaratne RJ. 1985. Identification and decarboxylase activities of bacteria isolated from decomposed mahimahi (Coryphaena hippurus) after incubation at 0 and 32° C. Int J Food Microbiol 2:331-40.
Fujii T, Kurihara K, Okuzumi M. 1994. Viability and histidine decarboxylase activity of halophilic histamine-forming bacteria during frozen storage. J Food Prot 57(7):611-3. Gale EF. 1946. The bacterial amino acid decarboxylases. Adv Enzymology and Related Subjects of Biochemistry 6:1-32.
Gessner BD, Hokama Y, Isto S. 1996. Scombrotoxicosis-like illness following the ingestion of smoked salmon that demonstrated low histamine levels and high toxicity on mouse bioassay. Clinical Infectious Diseases 23:1316-8.
Gildberg A. 1978. Proteolytic activity and the frequency of burst bellies in capelin. J Food Technol 13:409-16.
Gingerich TM, Lorca T, Flick GJ, Pierson MD, McNair HM. 1999. Biogenic amine survey and organoleptic changes in fresh, stored, and temperature-abused bluefish (Pomatomus saltatrix ). J Food Prot 62(9):1033-7.
Gloria MBA, Daeschel MA, Craven C, Hilderbrand Jr. KS. 1999. Histamine and other biogenic amines in albacore tuna. J Aqu Food Prod Technol 8(4):54-69.
Granerus G. 1968. Effects of oral histamine, histidine, and diet on urinary excretion of histamine, methylhistamine, and 1-methyl-4-imidazoleacetic acid in man. Scand J Clin Lab Invest Suppl 10(4):49-58.
Haaland H, Arnesen E, Njaa LR. 1990. Amino acid composition of whole mackerel (Scomber scombrus) stored anaerobically at 20° C and at 2 ° C. Int J Food Sci Tech 25:82-7.
Halasz A, Barath A, Simon-Sarkadi L, Holzapfel W. 1994. Biogenic amines and their production by microorganisms in food. Trends Food Sci Technol 5:42-9. Hardy R, Smith JGM. 1976. The storage of mackerel (Scomber scombrus). Development of histamine and rancidity. J Sci Food Agric 27:595-9.
Henry Chin KD, Koehler PE. 1986. Effect of salt concentration and incubation temperature on formation of histamine, phenethylamine, tryptamine and tyramine during miso fermentation. J Food Prot 49(6):423-7.
Hildrum KI, Scanlan RA, Libbey LM. 1976. Nitrosamines from the nitrosation of spermidine and spermine. In: Walker EA, Bogovski P, Griciute L, editors. Environmental N-Nitroso Compounds analysis and formation: proceedings of a working conference; 1975 Oct 1-3; Polytechnical Institute, Tallinn, Estonian SSR. International Agency for Research on Cancer. p 205-14.
Hui JY, Taylor SL. 1983. High pressure liquid chromatographic determination of putrefactive amines in foods. J AOAC 66(4):853-7.
Hungerford JM, Arefyev AA. 1992. Flow-injection assay of enzyme inhibition in fish using immobilized diamine oxidase. Analytica Chimica Acta 261:351-9.
Ibe A, Saito K, Nakazato M, Kikuchi Y, Fujinuma K, Nishima T. 1991. Quantitative determination of amines in wine by liquid chromatography. J AOAC 74(4):695-8.
Ienistea C. 1973. Significance and detection of histamine in food. In: Hobbs BC, Christian JHB, editors. The microbiological safety of foods. New York: Academic Press. p 327-43.
Jorgensen LV, Dalgaard P, Huss HH. 2000. Multiple compound quality index for cold-smoked salmon (Salmo salar) developed by multivariate regression of biogenic amines and pH. J Agric Food Chem 48:2448-53.
Kaneko J, (PacMar, Inc., Honolulu, Hawaii). 2000. Development of a HACCP-based strategy for the control of histamine for the fresh tuna industry [A report by PacMar, Inc. pursuant to National Oceanographic and Atmospheric Administration]. Honolulu (Hawaii): PacMar. 2000 Jul 31. NOAA Award No. NA86FD0067. 48 p.
Karolus JJ, LeBlanc DH, Marsh AJ, Mshar R, Furgalack TH. 1985. Presence of histamine in the bluefish, Pomatomus saltatrix. J Food Prot 48(2):166-8.
Kim S-H, Ben-Gigirey B, Barros-Velazquez J, Price RJ, An H. 2000. Histamine and biogenic amine production by Morganella morganii isolated from temperature-abused albacore. J Food Prot 63(2):244-51.
Kimata M, Akamatsu M, Ishida Y, (Kyoto Daigaku. Shokuryo Kagaku Kenkyujo). Memoirs of the Research Institute for Food Science. Kyoto: Kyoto Univ. 1960. Report nr 20. Studies on the classification of the genus Proteus I. p 1-7.
Kimata M, Kawai A, (Kyoto Daigaku. Shokuryo Kagaku Kenkyujo). Bulletin of the Research Institute for Food Science. Kyoto: Kyoto Univ. 1953 Oct. Report nr 12. The production of histamine by the action of bacteria causing the spoilage of fresh fish, I. 29-33 p.
Klausen NK, Huss HH. 1987. Growth and histamine production by Morganella morganii under various temperature conditions. Int J Food Microbiol 5:147-56.
Klausen NK, Lund E. 1986. Formation of biogenic amines in herring and mackerel. Z Lebensm Unters Forsch 182(6):459-63.
Koutsoumanis K, Lampropoulou K, Nychas G-JE. 1999. Biogenic amines and sensory changes associated with the microbial flora of Mediterranean Gilt-head sea bream ( Sparus aurata ) stored aerobically at 0, 8, and 15o C. J Food Prot 62(4):398-402.
Leitao MFF, Baldini VLS, Sales AM. 1983. Histamina em pescado e alimentos industrializados. Col Inst Technol Alim 13:123-30.
Leroi F, Joffraud JJ, Chevalier F. 2000. Effect of salt and smoke on the microbiological quality of cold-smoked salmon during storage at 5° C as estimated by the factorial design method. J Food Prot 63(4):502-8.
Leroi F, Joffraud JJ, Chevalier F, Cardinal M. 1998. Study of the microbial ecology of cold-smoked salmon during storage at 8° C. Int J Food Microbiol 39:111-21.
Leuschner RGK, Hammes WP. 1999. Formation of biogenic amine in mayonnaise, herring and tuna fish salad by Lactobacilli. Int J Food Sci Nut 50:159-64.
Lopez-Sabater EI, Rodriguez-Jerez JJ, Hernandez-Herrero M, Mora-Ventura MT. 1994a. Evaluation of histidine decarboxylase activity of bacteria isolated from sardine (Sardina pilchardus) by an enzymic method. Lett Appl Microbiol 19:70-5.
Lopez-Sabater EI, Rodriguez-Jerez JJ, Roig-Sagues AX, Mora-Ventura MAT. 1994b. Bacteriological quality of tuna fish (Thunnus thynnus) destined for canning: effect of tuna handling on presence of histidine decarboxylase bacteria and histidine level. J Food Prot 57(4):318-23.
Lopez-Sabater EI, Rodriguez-Jerez JJ, Hernandez-Herrero M, Mora-Ventura MT. 1996a. Incidence of histamine-forming bacteria and histamine content in scombroid fish species from retail markets in the Barcelona area. Int J Food Microbiol 28:411-8.
Lopez-Sabater EI, Rodriguez-Jerez JJ, Hernandez-Herrero M, Roig-Sagues AX, Mora-Ventura MT. 1996b. Sensory quality and histamine formation during controlled decomposition of tuna (Thunnus thynnus). J Food Prot 59(2):167-74.
Maga JA. 1978. Amines in foods. CRC Crit Rev Food Sci Nutr 10:373-403.
Masson F, Talon R, Montel MC. 1996. Histamine and tyramine production by bacteria from meat products. Int J Food Microbiol 32:199-207.
Mazorra-Manzano MA, Pacheco-Aguilar R, Diaz-Rojas EI, Lugo-Sanchez ME. 2000. Post mortem changes in black skipjack muscle during storage in ice. J Food Sci 65(5):774-9.
Mendes R. 1999. Changes in biogenic amines of major Portuguese bluefish species during storage at different temperatures. J Food Biochem 23:33-43.
Mendes R, Goncalves A, Nunes ML. 1999. Changes in free amino acids and biogenic amines during ripening of fresh and frozen sardine. J Food Biochem 23:295-306.
Middlebrooks BL, Toom PM, Douglas WL, Harrison RE, McDowell S. 1988. Effects of storage time and temperature on the microflora and amine development in Spanish mackerel (Scomberomorus maculatus). J Food Sci 53(4):1024-9.
Mietz JL, Karmas E. 1977. Chemical quality index of canned tuna as determined by high-pressure liquid chromatography. J Food Sci 42:155-8.
Mietz JL, Karmas E. 1978. Polyamine and histamine content of rockfish, salmon, lobster, and shrimp as an indicator of decomposition. J AOAC 61(1):139-45.
Morii H, Cann DC, Taylor LY, Murray CK. 1986. Formation of histamine by luminous bacteria isolated from scromboid fish. Bull Japan Soc Sci Fish 52(12):2135-41.
Murray CK, Hobbs G, Gilbert RJ. 1982. Scombrotoxin and scombrotoxin-like poisoning from canned fish. J Hyg 88:215-20.
Mutluer B, Ersen S, Kaya B, Akin S, Ozta-Siran I. 1989. Einfluss von Gammastrahlen auf Histaminbildung in Makrelenfilets. Fleischwirtsch 69:112-4.
Okuzumi M, Fukumoto I, Fujii T. 1990. Changes in bacterial flora and polyamines contents during storage of horse mackerel meat. Nippon Suisan Gakkasishi 56(8):1307-12.
Okuzumi M, Yamanaka H, Kubozuka T. 1984. Occurrence of various histamine-forming bacteria on/in fresh fishes. Bull Jap Soc Sci Fish 50(1):161-7.
Petaja E, Eerola S, Petaja P. 2000. Biogenic amines in cold-smoked fish fermented with lactic acid bacteria. Zeit Leben-Unter Forch 210(4):280-5.
Price RJ, Melvin EF, Bell JW. 1991. Postmortem changes in chilled round, bled and dressed albacore. J Food Sci 56:318-21.
Reddy NR, Armstrong DJ, Rhodehamel EJ, Kautter DA. 1992. Shelf-life extension and safety concerns about fresh fishery products packaged under modified atmospheres: a review. J Food Safety 12:87-118.
Ritchie AH, Mackie IM. 1980. The formation of diamines and polyamines during storage of mackerel (Scomber scrombrus). In: Connell J, editor. Advances in Fish Science and Technology. Surrey (England):Fishing News (Books) Ltd. P 489-94.
Rodriquez-Jerez JJ, Mora-Ventura MT, Lopez-Sabater EI, Hernandez-Herrero M. 1994. Histidine, lysine, and ornithine decarboxylase bacteria in Spanish salted semi-preserved anchovies. J Food Prot 57(9):784-7, 791.
Rogers, Staruszkiewicz. 1997. Collaborative study - GLC determination of cadaverine and putrescine in seafood; fluorometric method for histamine in tuna and mahimahi. JAOAC 80:591-602.
Shalaby AR. 1996. Significance of biogenic amines to food safety and human health. Food Res Int 29(7):675-90.
Shewan JM, Liston J. 1955. A review of food poisoning caused by fish and fishery products. J Appl Bacteriol 18:522-34.
Silla Santos MH. 1996. Biogenic amines: their importance in foods. Int J Food Microbiol 29:213-31.
Silva CCG, Da Ponte DJB, Enes Dapkevicius MLN. 1998. Storage temperature effect on histamine formation in big eye tuna and skipjack. J Food Sci 63(4):644-7.
Sjaastad O. 1966. Fate of histamine and N-Acetylhistamine administered into the human gut. Acta Pharmacol Toxicol 24:189-202.
Soares VFM, Gloria MBA. 1994. Histamine levels in canned fish available in the retail market of Belo Horizonte, Minas Gerais, Brazil. J Food Comp Anal 7:102-9.
Suzuki S, Matsui Y, Takama K. 1988. Profiles of polyamine composition in putrefactive Pseudomonas type III/IV. Microbios Letters 38:105-9.
Suzuki S, Noda J, Takama K. 1990. Growth and polyamine production of Alteromonas spp. in fish meat extracts under modified atmosphere. Bull Fac Fish, Hokkaido Univ 41(4):213-20.
Takagi M, Iida A, Murayama H, Soma S. 1969. On the formation of histamine during loss of freshness and putrefaction of various marine products. Bull Fac Fish, Hokkaido Univ 20:227-34.
Taylor SL. 1986. Histamine food poisoning: toxicology and clinical aspects. CRC Crit Rev Toxicol 17(2):91-128.
Taylor SL, Guthertz LS, Leatherwood M, Lieber ER. 1979. Histamine production by Klebsiella pneumoniae and an incident of scombroid fish poisoning. Appl Environ Microbiol 37:274-8.
Taylor SL, Guthertz LS, Leatherwood M, Tillman F, Lieber ER. 1978. Histamine production by food-borne bacterial species. J Food Safety 1:173-87.
Taylor SL, Lieber ER. 1979. In vitro inhibition of rat intestinal histamine-metabolizing enzymes. Food Cosmet Toxicol 17:237-40.
Taylor SL, Speckhard MW. 1984. Inhibition of bacterial histamine production by sorbate and other antimicrobial agents. J Food Prot 47(7):508-11.
Taylor SL, Stratton JE, Nordlee JA. 1989. Histamine poisoning (scombroid fish poisoning): an allergy-like intoxication. Clin Toxicol 27(4&5):225-40.
ten Brink B, Damink C, Joosten HMLJ, Huis in 't Veld JHJ. 1990. Occurrence and formation of biologically active amines in foods. Int J Food Microbiol 11:73-84.
Veciana-Nogues MT, Marine-Font A, Vidal-Carou MC. 1997. Biogenic amines as hygienic quality indicators of tuna. Relationships with microbial counts, ATP-related compounds, volatile amines and organoleptic changes. J Agric Food Chem 45:2036-41.
Wei CI, Chen C-M, Koburger JA, Otwell WS, Marshall MR. 1990. Bacterial growth and histamine production on vacuum packaged tuna. J Food Sci 55(1):59-63.
Wendakoon CN, Murata M, Sakaguchi M. 1990. Comparison of non-volatile amine formation between the dark and white muscles of mackerel during storage. Nippon Suisan Gakkaishi 56(5):809-18.
Wendakoon CN, Sakaguchi M. 1992a. Effects of spices on growth of and biogenic amine formation by bacteria in fish muscle. In: Huss HH, Jakobsen M, Liston J, editors. Quality Assurance in the Fish Industry: Proceedings of an International Conference; 1991 Aug 26-30; Copenhagen (DK). Amsterdam: Elsevier; 1992. p 305-13 (Development in Food Sci series; 30).
Wendakoon CN, Sakaguchi M. 1992b. Non-volatile amine production in mackerel muscle during growth of different bacterial species. J Food Hyg Soc Jap 33(1):39-45.
Wendakoon CN, Sakaguchi M. 1993. Combined effect of sodium chloride and clove on growth and biogenic amine formation of Enterobacter aerogenes in mackerel muscle extract. J Food Prot 56(5):410-3.
Yamanaka H, Shimakura K, Shiomi K, Kikuchi T, Okuzumi M. 1987b. Occurrence of allergy-like food poisoning caused by "mirin"-seasoned meat of dorado (Coryphaena hippurus). J Food Hyg Soc Japan 28(5):354-85.
Yamanaka H, Shiomi K, Kikuchi T, Okuzumi M. 1982. A pungent compound produced in the meat of frozen yellowfin tuna and marlin. Bull Jap Soc Sci Fish 48(5):685-9.
Yamanaka H, Shiomi K, Kikuchi T, Okuzumi M. 1984. Changes in histamine contents in red meat fish during storage at different temperatures. Bull Jap Soc Sci Fish 50(4):695-701.
Zotos A, Hole M, Smith G. 1995. The effect of frozen storage of mackerel ( Scomber scombrus ) on its quality when hot-smoked. J Sci Food Agric 67(1):43-8.